Chapter 1 The Asian Fishery Crisis, Nutritional Unequal Exchange and Food Insecurity

In: Where Shrimp Eat Better than People
Authors:
Wilma A. Dunaway
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Maria Cecilia Macabuac
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Abstract

We provide an overview of Asian food security, with a focus on the significance of fisheries. After an overview of the extent of Asian hunger and malnutrition, we examine six threats to regional food security: fishery exporting, redirection of seafoods into nonfood exports, growing dependence on imports, depeasantization, ecological degradation, intra-national inequalities in food access and food losses due to waste. The worst nutritional shortfalls in these fisheries are high iron and high protein foods, largely because domestic fish consumption has dropped as exporting has risen. We introduce the notion of nutritional unequal exchange to explore how these fisheries “trade down” internationally, substituting high fat/sugar imports for their more nutritious exports. Indeed, the world food system is nutritionally bifurcated, grounded in insufficient resources and underconsumption for the hungriest producing zones and privileged overconsumption in the least hungry, richer zones that devour the most nutritiously valuable foods. The fisheries with the worst hunger indices also engage in nutritional unequal exchange in order to export high iron/protein commodities to regions of the world that experience far less hunger. Those less-hungry importers ship back commodities that offer little relief from food and nutritional shortfalls.

In a world of unparalleled rural production and productivity … the number of those living in varying degrees of food insecurity and chronic hunger … is historically unprecedented.

(HAROON AKRAM-LODHI AND CRISTOBAL KAY 2010: 41)

Economic growth is … not sufficient to accelerate reduction of hunger and malnutrition.

(Food and Agriculture Organization 2012b: 4)

A majority of the world’s hungry and malnourished people are concentrated in our target areas of study, i.e., those territories of East, South and Southeast Asia that produce more than three-quarters of the world’s fish and export nearly one-third of globally traded fishery commodities (see Table 1). Between 2000 and 2010, regional calories per capita fell below the average for all the world’s developing countries. Even though these Asians spent more than half their household budgets on food (FAO 2014a), one of every eight people in this region “goes to bed hungry” (ADB 2013: xv). Consequently, East, South and Southeast Asia are populated by two-thirds of the world’s hungry people (see Figure 1). How could this be the case? Between 2000 and 2010, food production rates expanded in twelve of these Asia fisheries, but crops and fishery commodities for export absorbed much of that increase.1

Consequently, there is a counterintuitive food security paradox in East, South and Southeast Asia. Regional food production rose from 0.8 tons per capita in 1990 to 1.1 tons per capita in 2009. This annual 1.7 percentage growth rate was greater than that of any other region of the world. As a result, this region’s share in world food output increased from 41 percent in 1995 to 46 percent in 2009 (ADB 2013). In 2011, these Asian fisheries accounted for a majority of the world’s wild outputs and more than two-thirds of aquaculture production (FAO 2012e). As the Asian Development Bank (2013: xv) observes, food security requires “much more than raising food production.” Despite rising food and fishery outputs and exports, the number of undernourished people increased between 1995 and 2005 (FAO 2010: 22), and high levels of serious nutritional deficiencies continued (Ramachandran 2007; FAO 2012b). In 2011, nine of the world’s low-income food-deficient countries were situated in South and Southeast Asia (FAO 2011a), accounting for 29 percent of world population. Even though households are dependent on fish for one-third to three-quarters of their animal protein, fishery products are so prioritized for export that they are too expensive for consumption by the poor and a sizeable segment of the middle classes (FAO 2012b). While distant consumers have enjoyed declining prices that derived from Asia’s expanding supply of finfish (e.g., tilapia), shellfish (e.g., shrimp), crustaceans (e.g., crabs) and mollusks (e.g., oysters), seafoods became scarcer locally, and domestic prices inflated within Asian low-income food-deficient countries, like Bangladesh and the Philippines (FAO 2019a). Even countries that appear to be food self-sufficient mask underlying food shortfalls. For example, India is celebrated as being food self-sufficient nationally, but a majority of its citizens acquire less than 90 percent of recommended daily caloric intake, fish consumption has declined sharply over the last decade, and protein and iron deficiencies are widespread (Reddy and Mishra 2009).

1 Trends in Asian Fishery Production and Nutritional Shortfalls

The most alarming levels of hunger occur in Bangladesh, Cambodia, India, and Pakistan. Bangladesh has one of the highest undernutrition rates in the world, with 40 percent of its population and 50 percent of its women absorbing fewer calories than are needed for healthy survival (see Table 2). In terms of economic productivity of adult citizens, malnutrition costs Bangladesh $1 billion annually (Toufique 2015). Nearly half its population is anemic, more than one-quarter of its citizens acquire inadequate food to support physical activity, and more than two-fifths of its children are underweight. Despite a decade of declining food production and growing dependence on food imports, Bangladesh exported 123,698 tons of fishery commodities and 127,508 tons of food crops, depriving each of its citizens of one kilogram of these foods. Even though a majority of its population is anemic and more than two-fifths of its children are underweight, India exported more than 15 million tons of food crops and fish, removing 13 kilograms per capita from the domestic food chain. Pakistan exported 11 kilograms per capita while 25 percent of its population receives inadequate calories for physical activity, and nearly one-third of its children are underweight. Similarly, one-quarter of Cambodians are undernourished, and a high percentage are anemic.2

TABLE 2

Indicators of food insecurity, 2016

Part A. Low human development Index
Fishery territory Global hunger index 2010 % average annual population growth, 2000–2010 % annual increase or (decrease) in food production, 2000–2010 % population below poverty at $2 PPP per day % employed in agriculture % population under-nourished (insufficient calories) % children under 5 underweight Iron deficiency Anemia: WHO severity rank
aBangladesh Alarming 1.6 (1.5) 47.5 47.5 26.0 41.3 Severe
Myanmar Serious 1.1 6.3 32.0 70.0 21.7 29.6 Severe
aNorth Korea Serious 0.5 (0.2) 41.0 23.4 39.7 18.8 High
aPakistan Alarming 1.5 0.7 45.1 45.1 25.0 31.3 High
Part B. Medium human development index
aCambodia Alarming 1.7 3.9 72.3 72.3 25.0 28.8 Severe
China-Mainland Moderate 0.5 3.9 36.7 36.7 11.6 4.6 Moderate
aIndia Alarming 1.3 4.5 53.1 53.1 19.0 43.5 Severe
aIndonesia Serious 0.9 4.1 38.3 38.3 11.9 17.5 Severe
aPhilippines Serious 1.8 2.2 33.2 33.2 15.9 20.7 High
aSri Lanka Serious 0.9 4.8 32.5 32.5 25.7 21.6 High
Thailand Moderate 0.5 3.3 38.2 38.2 16.0 7.0 Moderate
Vietnam Serious 1.0 3.8 49.5 40.5 12.5 20.2 High
Part C. High human development index
China-Taiwan Low 0.4 1.6 5.2 5.2 4.0 10.1 Mild
Japan Low –0.1 (1.3) 3.2 4.1 1.6 3.0 Mild
Malaysia Moderate 1.5 3.8 14.2 14.2 4.0 12.9 High
South Korea Low 0.2 0.4 6.6 6.6 2.3 11.2 Moderate

FAO low-income food-deficit countries (FAO 2011a). Global Hunger Indexes are from Concern Worldwide (2010).

SOURCES AND NOTES: AGGREGATION AND ANALYSIS OF DATA FROM ADB (2010), IFPRI (2012), HTTP://DATAWORLDBANK.ORG, FAOSTAT, UNITED NATIONS (2011), AND WHO (2008)

Indonesia, North Korea, Myanmar, the Philippines, Sri Lanka and Vietnam exhibit serious hunger indexes, indicating that 12 to 40 percent of their populations are undernourished, more than one-quarter of citizens routinely receive inadequate calories to sustain physical activity, and about one-fifth of children are underweight. North Korea is the most food insecure country in Asia, with 43 percent of its population undernourished and dependent on international food aid (Relief Web 2019). Despite a famine in the 1990s that caused millions of deaths (Noland et al. 2001) and unrelenting hunger since 2000, North Korea has exhibited declining food production, stagnating fishery outputs, and growing dependence on food imports (FAO 2012b). One-third of its population is anemic, one-fifth of its children are underweight, and more than one-fifth of its pregnant and lactating women are malnourished (FAO 2015).3 Despite those trends, North Korea exported more than 61 million tons of fish and food crops in 2010. More than one-fifth of the citizens of Myanmar lack sufficient calories to sustain physical activity while nearly one-third of its children are underweight. Even though a majority of its citizens are anemic, Myanmar exported more than 2.7 millions tons of foods, eliminating 46 kilograms of food per capita from the domestic supply. Even though one-third of Sri Lankans are anemic, the country shipped out nearly one million tons or 47 kilograms per capita. Despite significant expansion of food production since 2000, 13 percent of Vietnamese and 12 percent of Indonesians acquire insufficient calories to sustain physical activity, and one-fifth of the children of these countries are underweight. Despite these food insecurity indicators, Vietnam exported 6.2 million tons of food crops and seafoods, withdrawing 71 kilograms of food per capita from its citizens, one-third of whom are anemic. While Indonesia ranks among the world’s top food and fishery exporters (FAO 2012b), more than two-fifths of Indonesians are anemic. The country exported 21 million tons, narrowing the domestic food supply by 88 food kilograms per capita.

China, Malaysia and Thailand may exhibit moderate hunger indexes, but they are not food secure. China and Malaysia are net food importers while Thailand barely breaks even in its exchange of food exports and imports. All three countries could ameliorate domestic nutritional shortfalls by allocating less fish to export and nonfood uses (see Table 3). Even though one-third of its population is anemic, Malaysia exported 9.5 million tons of food crops and fish, amounting to 336 kilograms per capita, the highest food export rate of these Asian fisheries. Nearly one-fifth of Thai citizens lack access to sufficient calories to sustain physical activity, one-fifth to one-quarter are anemic, and the state must implement public strategies to overcome childhood nutritional problems (FAO 2012b). In the face of those hunger problems, Thailand shipped out nearly 15 million tons or 226 kilograms per capita, ranking it the third highest food exporter in these Asian fisheries. While China produced 49.2 kilograms per capita, only 27.2 of them were consumed by its citizens. Despite clear need for use of its resources domestically, China exported 24.5 million tons of food crops and fish or 18 kilograms per capita.

TABLE 3

What happens to fishery production? How exporting, nonfood uses and wastage threaten food security, 2016

Part A. Asian fisheries with alarming or serious global hunger index in 2010
Fishery territory MT edible fish produced Production KG per capita (MT edible fish exported) (MT nonfoods) (MT fishery wastage) MT production remaining for domestic consumption % production available for domestic consumption KG per capita available for domestic consumption KG above or (below) world per capita consumption
aBangladesh 3,878,324 23.8 71,976 32,264 1,241,064 2,533,020 65.3 15.5 (4.8)
aCambodia 802,450 50.7 26,601 79,197 256,784 439,868 54.8 27.8 7.5
aIndia 10,761,756 8.1 1,032,334 787,208 3,443,762 5,498,452 51.1 4.1 (16.2)
aIndonesia 11,492,258 44.1 836,898 930,204 3,677,523 6,047,633 52.6 23.2 2.9
Myanmar 3,090,004 56.8 329,096 677,461 988,801 1,094,646 35.4 20.1 (0.2)
aNorth Korea 247,100 9.8 58,840 27,030 79,072 82,158 33.3 3.3 (17.0)
aPakistan 376,391 2.0 131,747 114,831 120,445 9,368 2.5 0.5 (19.8)
aPhilippines 2,821,223 27.6 257,219 51,452 902,791 1,609,761 57.1 15.7 (4.6)
aSri Lanka 550,547 26.5 17,783 18,456 176,175 338,133 61.4 16.3 (4.0)
Vietnam 6,410,478 67.9 1,468,596 617,968 2,051,353 2,272,561 35.5 24.1 3.8
Part B. Asian fisheries with moderate global hunger index in 2010
China-Mainland 66,808,381 49.2 4,086,464 3,701,763 21,378,682 37,641,472 56.3 27.7 7.4
Malaysia 1,782,189 58.0 248,749 309,362 570,300 653,778 36.7 21.3 1.0
Thailand 2,493,154 36.6 1,353,863 563,488 797,809 222,006 8.9 3.3 (17.0)
Part C. Asian fisheries with low global hunger index in 2010
China-Taiwan 1,005,293 42.7 682,824 76,434 321,694 75,659 7.5 3.2 (17.1)
Japan 3,872,324 30.7 502,858 893,750 1,239,144 1,236,572 31.9 9.8 (10.5)
South Korea 1,894,408 37.5 485,027 177,098 606,210 626,073 33.1 12.4 (7.9)

low-income food-deficit countries (FAO 2011a). World per capita consumption = 20.3 KG. Global Hunger Indexes are from Concern Worldwide (2010).

SOURCES AND NOTES: ANALYSIS OF DATA THAT WERE AGGREGATED FROM GLOBAL FISHERY AND AQUACULTURE DATABASES, FAO. PHILIPPINE EXPORTS AND NONFOODS ARE FROM PHILIPPINE ANNUAL FISHERIES PROFILE (2016). NONFOODS WERE ESTIMATED USING THE LATEST FAO (2016: 67–68) FOOD BALANCE SHEETS. WASTE WAS ESTIMATED AT 32% (SEE FIGURE 11)

While Taiwan, Japan and South Korea exhibit low hunger indexes, they are far from food self-sufficient. Domestic food production has declined or stagnated over the last decade, as these countries have become increasingly dependent on food imports (FAO 2012b). Despite these trends, Japan exported more than 2 million tons of foodstuffs, a majority of it in fishery products. Even though Japan produced 30.7 kilograms of fish and shellfish per capita, its citizens had access to less than ten kilograms per capita (see Table 3). Even though South Koreans consume less than recommended levels of protein, vegetables and fruits (FAO 2012b) and exhibit a moderate incidence of anemia, the country exports more than 3 million tons or 61 kilograms per capita. While South Korea produced 37.5 kilograms of fish and shellfish per capita, only one-third of those foods were available for domestic consumption (see Table 3).

1.1 Child Food Insecurity

Despite rapid growth of regional food exports (FAO 2012b), Asia is ranked as one of the world’s hot spots of child malnutrition and food insecurity. Ramachandran (2007: 219) observes that:

endemic pockets of hunger remain, seasonal shortfalls are manifest, and malnutrition is widespread across the region, women and children being the greatest sufferers. The Asian enigma, as it is termed, has defied all attempts at resolution so far. Poverty alleviation strategies, livelihood generation programmes and direct food interventions have all been tried, to little avail. … Even most food deficit countries of sub-Saharan Africa score higher in terms of nutrition levels of their women and children.

Throughout Asia, the incidence of under-nutrition among rural children younger than twelve is alarmingly high, and half of them are so under-weight and stunted they are harmed for life (McLean et. al 2009; Saxena 2008).

1.2 Iron Deficiency Anemia

Two-thirds of Asian preschool children and two-thirds of Asian pregnant and lactating women are anemic (McLean et. al 2009; IFPRI 2016). Indeed, iron deficiency anemia is feminized. The incidence of female anemia is severe (impacting 41 percent or more) throughout South and Southeast Asia and high (impacting 30 to 40 percent) throughout East Asia (McLean et. al 2009).4 Two-fifths to nearly half the females of Bangladesh, India, Indonesia, Myanmar, and the Philippines suffer from anemia (McLean et. al 2009). This nutritional disease impacts females who reside in Malaysia and Pakistan to about the same degree, even though these countries vary significantly in incidence of poverty and economic growth. China, South Korea and Vietnam are experiencing rapid entry of women into the industrial labor force, but they exhibit female anemia at about the same level as Thailand and Sri Lanka which are much less industrialized. China, Malaysia, Thailand, South Korea and Japan receive moderate to low hunger indexes, but these countries exhibit higher incidence of female anemia than any other food insecurity indicator (see Table 2). In China, for example, the percentage of anemic pregnant women is 2.5 times greater than the percentage of the population that is undernourished.

1.3 Asian Fishery Production and Nutritional Trends

It is quite striking that Asian fisheries that differ sharply in economic growth rates and degrees of industrialization exhibit similar trends with respect to food insecurity indicating that increased trade and prosperity have not solved national hunger problems. In addition to widespread inadequate calorie intake, most Asians secure 60 percent of their calories from carbohydrates (primarily grains), leading to significant shortfalls of protein, iron and other essential nutrients (FAO 2012b: 9, 15–16). As a result, the four most widespread nutritional deficiencies in Asia are inadequate levels of protein, iron, Vitamin A and iodine, shortfalls that are suffered most extremely by rural women and children (ESCAP 2010). In addition to a high incidence of iron deficiency anemia, 72 percent of preschool children and 60 percent of pregnant women exhibit Vitamin A deficiency, the most common cause of blindness and a contributing factor in infant mortality and childhood growth retardation.5 In South and Southeast Asia, there is a high incidence of iodine deficiency, the main cause of mental retardation.6 Across Asia, the most abundant foods available to address these nutritional deficiencies are fishery derivatives, but current health trends make it clear that a high proportion of Asians are not consuming the seafoods in which their fisheries specialize.

In 2010, Asia accounted for 60.8 percent of the world’s fish that were captured in oceans and coastal waters, 43 percent of fish captured from inland rivers, and 89 percent of aquaculture outputs (FAO 2012d). More than half of the world’s captured fish are produced by our target sixteen Asian fisheries which are among the world’s most significant fishery exporters.7 More than 87 percent of people employed in the fisheries sector in 2010 were in Asia, and 97 percent of all fish farmers were Asians. However, thirteen of these fisheries exhibit moderate to alarming hunger indexes (see Table 2), and seven of them are classified by the Food and Agriculture Organization as low-income food-deficient nations. Similarly, fourteen of these Asian fisheries ranked among the top thirty aquaculture producers in the world, but five of these high exporters were food-deficient.8

2 Investigative Questions

Obviously, we should question why significant nutritional shortfalls are occurring in the very region that generates a majority of the world’s fishery and aquaculture production. Since domestic consumption of agricultural and fishery production could be significant in the alleviation of Asian undernutrition and shortfalls of protein, iron, Vitamin A and iodine, we will explore eight questions:

  1. To what extent is food and fishery exporting a food security problem?

  2. Will dependence on imports solve Asian food security problems?

  3. To what degree do production of and conversion to nonfoods threaten Asian food security?

  4. Will aquaculture solve Asian nutritional shortfalls?

  5. How does depeasantization threaten Asian food security?

  6. To what extent does ecological degradation of fisheries threaten Asian food security?

  7. How do intra-national inequalities complicate Asian food insecurity?

  8. What are the impacts of wastage on Asian food security?

3 Conflict between Food Security and Food/Fishery Exporting

Philippine scholar Renato Constantino (1988: 17) contends that: “the principal bait for the shift to export crops is the prospect of foreign exchange to repay external debts.” By the turn of the 21st century, fourteen of the Asian fisheries were trapped in a vicious circle of debt/trade/more debt (SAPRIN 2004). Their export strategies are designed to accumulate foreign exchange to repay loans that were incurred to fund export agendas that, in turn, may not generate enough revenue to offset those transnational debts (Tyner 2004). Between 1990 and 2010, East Asian countries expanded their debt fourteenfold, South Asian nations more than doubled their debt load, and Southeast Asian states expanded their debt 154 percent. By 2010, debt represented more than 38 percent of Gross National Income of South Asian countries and nearly 40 percent of Southeast Asian GNI. In the face of high levels of poverty and hunger, debt ratios per capita are staggering: $1,283 for East Asians, $246 for South Asians, and $751 for Southeast Asians. In South Asia where hunger is most problematic, national debt averages 69 percent of the Gross Domestic Product. In Asian low-income food-deficient countries, national debt averages 67 percent of the Gross Domestic Product.9

To implement structural adjustment goals set by the IMF and the World Bank, Asian fisheries have targeted their ecological resources, expanded their food exports, and deepened their integration into the world agro-industrial food system. Following guidance from the IMF and World Bank since the early 1990s, Asian fisheries have redirected their agricultural growth into production of export commodities that are expected to generate foreign exchange for debt repayment (Tyner 2004). Despite serious hunger problems, Asian governments have allocated agricultural lands to nonfood crops, livestock pastures and fishponds in order to prioritize export of a higher percentage of their food and fishery production. Such structural adjustment programs have led to increased hunger throughout a majority of these Asian fisheries. “Adjustment measures have been designed based on the assumption that local supply is not important, as access to food could be obtained through the market” (SAPRIN 2004: 8, 140). This philosophy is grounded in two key neoliberal notions, i.e., that trade is the central food security solution and that the success of any food security strategy is measured by its positive impacts on economic growth (Guha-Khasnobis et al. 2007: 307–309). To complicate matters, these Asian fisheries have increased food importing to comply with World Trade Organization rules, further threatening the declining incomes of rural Asian households (GuhaKhasnobis et al. 2007; SAPRIN 2004).

3.1 Fishery Exporting

In 2016, thirteen of these sixteen Asian fisheries ranked among the world’s top fifty exporters (see Table 1). In line with structural adjustment and WTO requirements, they expanded their fishery and food crop exporting since 1985 (FAO 1989, 2012e), even though all of them except Japan have experienced hunger crises during this period. Despite their alarming, serious or moderate hunger indexes, India, Indonesia, Malaysia, Myanmar, Sri Lanka, Thailand and Vietnam attained trade surpluses in exchanges of food commodities. Trade statistics make clear the food insecurity of four countries that are experiencing alarming or serious hunger problems. While China, Japan, and South Korea exchange manufactured goods for food imports, Bangladesh, North Korea, Pakistan, and the Philippines exhibit large food trade deficits. Since 1975, fishery and aquaculture outputs have expanded sufficiently to alleviate many of the region’s nutritional problems (Hersoug 2004: 59), but much of that output has been exported (APFC 2012). Between 1988 and 2002, the value of fishery exports from many developing countries exceeded the value of other agricultural commodities (Eggert and Greaker 2009: 1). Indeed, these sixteen Asian fisheries prioritize seafood exporting because shellfish are more valuable per ton on world markets than agricultural crops (see Figure 5).

FIGURE 5
FIGURE 5

The economic importance of crustacean exports: $US per exported ton of commodities, 2016

SOURCE AND NOTES: ANALYSIS OF EXPORT DATA THAT WERE AGGREGATED FROM UNCOMTRADE DATABASE

3.2 Threats to Asian Agricultural Production

The food security threats associated with fishery exporting are exacerbated by the elimination of agricultural space. In all the Asian fisheries, national and local governments have stimulated the conversion of croplands and domestic-oriented aquaculture to commercial fishponds (Bailey and Skladany 1991; Primavera 1997; FAO 2004a, 2007). In the face of expansion of commercial fishponds and other nonagricultural demands, expanding cultivated lands for food production is no longer an option in the sixteen Asian fisheries where arable land declined from 0.36 hectares in 1970 to 0.20 in 2011. East and Southeast Asia have suffered a 37 percent decline in arable lands while arable lands dropped 58 percent in South Asia. Moreover, gains from the artificial inputs of the Green Revolution waned in the 1990s, making declining yields per hectare common (ADB 2013: 40–43). To complicate matters, most arable farm lands are not used to cultivate crops for domestic consumption.

When we compare agricultural exports (United Nations 2013) with crop production data (FAO 2012c), it becomes clear that these Asian fisheries prioritize crops for export rather than domestic food security. Fourteen of them allocate more of their agricultural lands to the production of carbohydrates and sugar than to food crops that will address nutritional problems. Grains, sugar cane/beets, bananas, coconuts, and vegetables address some local consumption needs, but these crops are exported at high levels. Only China, Japan, North Korea and South Korea cultivate non-starchy vegetables as one of their three most important crop categories that can be applied toward domestic consumption. Food security is further threatened because less of the agricultural land is allocated to the production of food crops than to nonfoods (see Table 10). For example, food-deficient Sri Lanka allocates a majority of its lands to the production of tea while food-deficient India, Indonesia and the Philippines allocate significant land resources to cultivation of cotton, palm oil, rubber, and tobacco. Moderately food-insecure Malaysia depends on food imports while it utilizes most of its agricultural lands to cultivate palm oil and rubber for export.

3.3 Centrality of Fishery Outputs to Asian Nutrition

Bottom line, there is no significant crop production in any of these Asian fisheries that will offset the losses of protein, iron and other nutrients that result from fishery exporting. Except for Japan and Taiwan, all these fisheries exhibit a moderate to severe incidence of iron deficiency anemia (see Table 2). Fishery products are the resources most readily available that could be locally consumed to overcome their widespread protein, iron and iodine shortfalls (McLean et al. 2009). Table 3 provides a sharp analysis of the threats to Asian food security posed by export of fishery products. When wastage and nonfood uses are taken into account, none of these Asian fisheries produces enough fish to meet domestic needs. In reality, so much fishery output is lost to wastage that there is no latitude for nonfood uses or exports. It is clear, however, that these Asian fisheries are prioritizing exports and nonfood applications over domestic consumption. In 2016, per capita world consumption of fishery commodities rose to 20.3 kilograms. It is reasonable to expect that domestic consumption in these Asian fisheries should exceed that global average, but that is not the case. Eight of the ten Asian fisheries with alarming or serious hunger indexes consumed less than the typical world citizen (see Table 3). Fishery commodities are barely consumed in India, Pakistan and Thailand where they could help to alleviate moderate to alarming hunger indexes. In Bangladesh, Pakistan, North Korea, Thailand, Taiwan, Japan, South Korea, the Philippines and Sri Lanka, domestic consumption per capita is half or less than it was in 1961 (Kent 2018).

Three cautions about methodological flaws are in order with respect to Table 3. First, FAO estimates of nonfoods are low, based primarily on reservations for seeds and feeds at production sites. Indeed, the FAO Food Balance Sheets from which we drew data do not include conversion into nonfoods after leaving the production sites. Second, the FAO has only recently begun to estimate losses at the production sites, but Food Balance Sheets do not estimate fishery wastage after commodities leave the production sites. For that reason, we employed wastage estimates from the most recent research about Asian countries. Third, FAO export numbers are not always reliable, and it is likely that more fish were exported from these Asian territories than the FAO Food Balance Sheets report. According to the Food and Agriculture Organization (2012b: 41, 58), nearly 60 percent of the world’s captured and farmed fish are destined for export. Since a majority of the world’s fishery production occurs in these sixteen Asian fisheries, it is likely that the FAO (2012e) national exporting proportions that we used for this table are lower than the actual levels. Indeed, export quantities for these Asian fisheries are often higher in the UN COMTRADE International Trade Statistics database. By repeating these FAO methodological flaws, a majority of analysts who study Asian food security offer optimistic estimates about per capita domestic consumption because they ignore or seriously underestimate exports, nonfood uses and wastage.10

Table 4 demonstrates that consumption of fishery commodities has declined below FAO estimates. Since the early 1990s, fishery consumption per capita has steadily declined in these Asian fisheries, as exporting has led to rising domestic prices, especially for shellfish (Mulekom et al. 2006: 554–55). By 2010, average Asian per capita fish consumption was much lower than the consumption levels of North Americans and Europeans. Bangladesh, India, Indonesia, Myanmar, Pakistan and Vietnam fall well below average per capita consumption reported by the FAO (2012d) for Asia. Moreover, per capita fish consumption for India and Pakistan is about one-fifth of the average per capita consumption reported by FAO (2012d) for all low-income food-deficient countries. Despite its production and high export levels, Pakistan now exhibits the lowest per capita consumption of fish in the world. Even though India is the seventh top ocean fish producing country (Siar and Kusakabe 2020: 23), most Indians have included very little fish in their diets since the shift to shrimp exporting in the early 1980s. In 1980, the largest peasant fisher’s organization publicly protested against the Indian government’s establishment of a multi-million dollar fishing complex at Bombay, emphasizing the danger of the country’s shift to prioritizing exporting.

TABLE 4

Per capita dietary protein consumption, 2013

Territory % fish protein % animal protein % plant protein
Bangladesh 10.4 18.5 71.1
Cambodia 20.0 29.1 50.9
China-Mainland 9.1 40.5 50.4
China-Taiwan 9.6 48.1 42.3
India 3.0 20.3 76.7
Indonesia 16.3 26.0 57.7
Japan 20.0 55.3 24.7
Malaysia 21.6 55.6 22.8
Myanmar 19.8 42.6 37.6
North Korea 5.4 18.8 75.8
Pakistan 1.0 41.7 57.3
Philippines 14.9 41.1 44.0
South Korea 16.4 48.0 35.6
Sri Lanka 15.3 27.5 57.2
Thailand 13.5 40.5 46.0
Viet Nam 11.2 52.9 35.9

SOURCE: ANALYSIS OF FOOD BALANCE STATISTICS, FAOSTAT

The developed world is now making strident demands for our fish varieties. … If this trend continues, the Indian population will have to do without fish since the foreign buyers are ready to pay ten times the amount a poor Indian could afford. Can we allow our fish which is our vital food resources to be exported at the cost of the protein-starved population of our country, even if the principle involved is the highly questionable foreign exchange earnings?11 (Kent 2018: 19)

In 2012, domestic fish prices were 1.4 times greater than beef and 1.5 times greater than chicken. As a result, India ranks 116 out of 160 countries in its per capita consumption of fish (Indian Dept. of Fisheries 2019), and two coastal provinces account for 90 percent of Indian fishery consumption (Kent 2018: 85–88).

Similarly, North Koreans could not possibly be consuming the 45 kilograms per capita estimated by FAOSTAT. In short, most of these fisheries are able to export because they withdraw resources from the domestic consumption pool. Indeed, fish and shellfish shortfalls have been reported in newspaper and NGO accounts since the mid-1990s (Wilks 1995; Environmental Justice Foundation 2003; Wilkinson 2010). Whatever the optimistic statistical estimates indicate, there is a more empirical barometer of the degree to which Asians lack access to the fish produced domestically. Declining consumption of indigenous high-protein, high-iron fish lies at the heart of the high to severe incidence of anemia and protein shortfalls in most of these Asian fisheries (see Table 2), as well as the high incidence of iodine and Vitamin A deficiencies.12 If there were not large segments of the Asian populations that eat very little of the high-iron finfish, shellfish, and mollusks, national levels of these nutritional shortfalls would not be so high among Asian women and children. On average in 2013, fish accounted for only 12.9 percent of protein consumed in the Asian fisheries, showing a clear trend toward substitution of animal and plant proteins.

4 Dependence on Imports as Threat to Food Security

Worldwide disparities among income levels produce unequal exchange, the structural process through which capitalists drain off an inequitable share of economic surpluses (Emmanuel 1972: 371–2). According to Donald Clelland,

This unequal exchange occurs because of the super-exploitation of peripheral labor, resources and environment. By its logic, unequal exchange is not just about international trade or even trade between unequally developed regions. It is about unequal exchange (conflict) between higher income and lower income sectors in different areas of the world-system. Workers who do the same tasks with similar equipment earn income levels that differ by as much as a ratio of fifty to one or more between zones. Fundamentally, unpaid and under-paid labor and natural resources are derived from worker households and communities that are not remunerated at a level that will cover the actual costs of their survival and reproduction. I refer to these unpaid labors and resources as dark value drains that are hidden, uncosted, embedded in cheap consumer prices, and concealed in profit accumulation. The uncosted peripheral hours remain embedded in the purchased product but are not reflected in the price of the product. As a result, the worker in a rich country becomes an unwitting beneficiary of this unequal exchange. He/she can purchase for one waged hour of his/her own work food that requires ten lower-waged hours of peripheral labor.13

Consequently, the unequal exchanges and dark value drains (Clelland 2013, 2014) within the commodity chains of the global food trade generate disproportionate per capita consumption by the richest countries and under-consumption by the developing countries– in terms of both calorie intake and nutrient density. Through nutritional unequal exchanges between richer countries and developing countries, the richer countries acquire a disproportionate share of the world’s most nutritious foods at very cheap costs, so they exhibit the lowest levels of domestic malnutrition.14 We should think of these nutritional unequal exchanges as a regime of forced underconsumption. Indeed, the world food system is nutritionally bifurcated, grounded in insufficient resources and “coerced underconsumption” for the hungriest producing zones and “privileged overconsumption” in the least hungry, richer zones that devour the most nutritiously valuable foods (Araghi 2009: 120, 142) By lowering the household consumption of laboring fishers, these inequitable trading patterns increase capitalist profits by causing hunger and malnutrition.

Moreover, greater ecological degradation is externalized to the hungrier, producing zones. Harriet Friedmann (1992) refers to ecologies at a distance because nutrients and their embedded labor power are exported far from the producing areas that bear the brunt of natural resource drains and environmental damage. Through this ecological unequal exchange, there is “environmentally damaging withdrawal of energy and other natural resource assets.” However, richer countries that consume the highest levels of natural resources “are typically characterized by the lowest domestic levels of environmental degradation” (Jorgensen and Rice 2012: 432). For example, countries that import palm oil externalize to the producing countries loss of vast areas of forest and the displacement of thousands of food-producing peasant households (Sommer et al. 2020; Gellert 2015; Hall 2011). In similar fashion, market prices do not take into account the full ecological cost of fishing. Distant consumers

do not pay for the cost of the future reproduction [that] the fish will no longer accomplish, or the cost of ecosystem disruption from overfishing, or the other fish or bird species that were caught incidental to the catching of that fish. And [consumers] certainly do not pay for the harm that fishing technologies impose on the ecosystem. (DeSombre and Barkin 2011: 19)

While several Asian governments have established rice controls and consumer subsidies (FAO 2003c: 188–96), no Asian state regulates fish in ways that prioritize local consumption. As a result, more than two-thirds of the 2012 Asian fishery exports were marketed to developed countries that do not have food shortfalls (FAO 2012b: 41, 70). In 2017, the Asian fisheries marketed a majority of their exports to countries that exhibited low hunger indexes (see Table 5). Seven of the ten countries with serious to alarming hunger indexes marketed more than three-quarters of their fishing commodities to western, Middle Eastern and Asian low hunger zones. With moderate hunger indexes, China, Malaysia and Thailand, exported three-fifths to three-quarters of their fishery commodities to low hunger western countries and to Japan, Taiwan and South Korea. In short, Asian fisheries are feeding over-nourished buyers who have sufficient food intake without Asian exports while their own citizens face nutritional shortfalls. Even though they produced nearly two-thirds of the world’s seafoods in 2016, these Asian fisheries fell below or only slightly above average world per capita consumption of the finfish, shellfish and mollusks they exported. Indeed, eight of the fisheries with the worst Hunger Indexes fell below the world consumption average. Despite their low hunger indexes, their high incomes and their traditional high-fish diets, Taiwan, Japan, and South Korea fell significantly below world per capita consumption (see Table 3). Clearly, all these Asian fisheries are shifting away from traditional patterns of healthy fish consumption (see Table 4) in order to export their outputs to areas of the world that are experiencing little hunger (see Table 5).

TABLE 5

Nutritional unequal exchange: Exports of fishery foods from high hunger zones to low hunger zones, 2017

Part A. Asian fisheries with alarming or serious global hunger index in 2010
Country ranked alarming or serious on the 2010 global hunger index % fishery exports to western low hunger zones % fishery exports to Asian low hunger zones % fishery exports to Middle Eastern low hunger zones % fishery exports to Asian moderate hunger zones Total % of fishery exports to lower hunger zones
Bangladesh 77.3 4.6 0.3 13.3 95.5
Cambodia 6.0 94.0 94.0
India 48.8 8.3 3.5 36.3 96.9
Indonesia 50.5 20.8 0.2 21.4 92.9
Myanmar 18.6 20.5 47.9 87.0
North Korea 0.2 47.9 99.6
Pakistan 2.0 3.1 14.6 71.3 91.0
Philippines 33.7 26.7 12.5 72.9
Sri Lanka 60.8 17.6 8.0 4.1 90.5
Viet Nam 15.5 39.7 1.2 27.2 83.6
Part B. Asian fisheries with moderate global hunger index in 2010
China-Mainland 31.1 43.2 74.3
Malaysia 11.1 45.8 0.7 57.6
Thailand 35.5 37.9 1.0 74.4

SOURCES: ANALYSIS OF THE LIST OF THE TOP 25 IMPORTING MARKETS FOR THE FISHERY EXPORTS OF EACH COUNTRY (SHOWING $US VALUE), TRADE INDICATORS, TRADE MAP DATABASE, INTERNATIONAL TRADE CENTRE. GLOBAL HUNGER INDEXES ARE FROM CONCERN WORLDWIDE (2010).

4.1 How Is the Food Import Budget Spent?

Since the late 1980s, United Nations policy has been grounded in the philosophy that economic globalization offers opportunities for integrating the rural poor and for achieving food security in the Global South. Consequently, the Food and Agriculture Organization advocates that

farmers need to develop a greater knowledge of global-agricultural trends in order to produce crops that will be competitive on the global market. …The FAO’s focus is less on how neoliberal and developmental economic theory/policy has contributed to hunger and poverty than on how globalization can benefit the poor through the implementation of new policies. … By avoiding a more rigorous critique of neoliberal and developmental economic theory, FAO remains married to the belief that economic growth, competition, efficiency, and profiteering hold the answer to achieving food security. (Schanbacher 2010: 9)

FAO policy emphasizes economic growth, integration into the global food trade system, and smallholder adaptation of imported Green, Blue and Genetic technologies. If trade liberalization worsens domestic conditions, the FAO explains, it is because national governments fail to offer social safety nets (FAO 2006a: 30–31), not because the global economic development agenda is biased in favor of the richest countries and their massive agribusinesses.

Consequently, the 1996 World Food Summit grounded global food security in the market-oriented world trade system. The 186 country representatives agreed that “trade is a key element in achieving world food security.” According to their reasoning, trade “allows domestic food consumption to be met more cheaply by less costly imported supplies,” and it “increases consumer choice by providing access to a greater range and diversity of foods” (World Food Summit 1996: Point 3.6). It is striking that the World Food Summit ignored price instabilities in the world food trade. Rising and erratic food prices represent a major risk facing Asian countries that depend on food imports (FAO 2019a). The food price index barely changed in developed countries over the decade between 2002 and 2012. Consumers in richer countries, including Japan, benefitted from stable pricing and from the cheap export prices of developing countries. In contrast, food prices were erratic and inflationary (and volatile from month to month) for the Asian fisheries.15 Moreover, delegates overlooked an even more significant problem. The stated policies reflect no concern about whether countries would acquire, through importing, the foods they need to address domestic nutritional shortfalls associated with hunger and disease. Nor did the Summit question whether the capitalists buying foreign foods for resale would select the kinds of nutrients most needed to address domestic needs (Watkins 1996).

Do the Asian fisheries overcome domestic dietary shortfalls through imports, as the FAO (2012d) claims will happen? Table 6 provides an empirical assessment of whether East, South and Southeast Asia import high levels of foods that supply the nutrients missing from domestic production and/or drained away by exporting. Even though the food-deficient fisheries exhibited high per capita deficits of high iron/protein foods, they did not prioritize those nutritional shortfalls. On average in 2016, they expended nearly 78 percent of their food import budgets on high fat/sugar and non-caloric foods and less than 10 percent to acquire high iron/protein foods. Despite its serious hunger index, Myanmar was the most extreme outlier because nearly 99 percent of its imports were high fat/sugar commodities and only one percent were high iron/protein foods. This trend reflects the global homogenization of dietary consumption and capitalist marketing to wealthier consumers. In 2011, ten commodities accounted for more than 80 percent of the world’s trade foods, and the trading of oils and fats grew faster than any other traded foods (Falconi et al. 2017: 147). Throughout the sixteen Asian fisheries, “much of the foreign exchange earned from the export of foods is not devoted to purchasing low cost nutritive foods for the needy, but is diverted to the purchase of luxury foods and other products in demand by local elites” (Mulekom et al. 2006: 550).

TABLE 6

How is the import budget spent? Percentage of total value expended by food category, 2016

Part A. Asian fisheries that were classified as food deficient by FAO in 2010
Fishery territory High iron & high protein foods Vegetables & fruits (not high protein) Foods that convert to sugars & fats in the human body Non-caloric coffee, tea, spices & yeast % All food imports that are processed
A aBangladesh 3.1 20.9 72.0 4.0 8.7
A aCambodia 8.6 9.5 81.5 0.4 3.9
A aIndia 9.2 18.9 69.2 2.7 6.4
A aPakistan 3.2 13.0 78.5 5.3 8.1
S aIndonesia 20.9 12.2 65.3 1.6 26.7
S aNorth Korea 13.0 10.0 72.4 4.6 38.2
S aPhilippines 15.2 4.2 77.7 2.9 36.3
S aSri Lanka 4.3 11.4 69.2 15.1 14.5
Part B. Asian fisheries that were not classified as food deficient by FAO in 2010
S Myanmar 1.0 0.3 97.2 1.5 45.3
S Vietnam 18.0 6.3 72.5 3.2 32.5
M China-Mainland 59.5 2.9 35.9 1.7 13.1
M Malaysia 15.3 6.4 72.6 5.7 25.7
M Thailand 44.5 3.9 48.2 3.4 33.2
L China-Taiwan 29.3 14.4 54.0 2.3 26.3
L Japan 30.3 34.0 33.2 2.5 26.7
L South Korea 34.3 4.4 58.0 3.3 24.1

low income food deficient countries (FAO 2011a).

SOURCES AND NOTES: ANALYSIS OF IMPORTS AGGREGATED FROM UN COMTRADE DATABASE. HIGH IRON AND PROTEINS INCLUDE MEATS, FISH, NUTS, EGGS, MILK PRODUCTS, LEGUMES AND SOYA. FOODS THAT ARE METABOLIZED BY THE HUMAN LIVER INTO SUGARS AND FATS INCLUDE RAW AND REFINED SUGARS, HONEY, MOLASSES, SUGAR-BASE PREPARATIONS AND BEVERAGES, FATS AND OILS, AND ALCOHOLIC BEVERAGES. THE LETTERS BEFORE NAMES REFER TO THEIR 2010 GLOBAL HUNGER INDEXES (CONCERN WORLDWIDE 2010); A = ALARMING, S = SERIOUS, M = MODERATE, L = LOW

Indeed, all ten fisheries ranked with alarming or serious hunger indexes experienced per capita deficits of high-iron foods and of nutrient dense fishery products. However, they expended two-thirds or more of their food import budgets on commodities that (a) lacked the nutrients to address domestic health shortfalls and (b) were unhealthy enough to generate new kinds of health problems. What we have found supports the growing body of scholarship that points to a double burden of malnutrition in developing countries in which traditional diets are being displaced by a global diet dominated by carbohydrates, fats and sugars. Undernutrition among the poor is accompanied by rising obesity rates and lifestyle diseases in the middle classes (Popkin 2001; Kennedy et al. 2004; Hawkes 2006; Khan and Khoi 2008).

China was the most extreme positive outlier, for it was the only Asian fishery that directly utilized trade to address shortfalls in high iron/protein nutrients. Nearly three-fifths of its imports were high iron/protein foods while nearly 38 percent were high fat/sugar and non-caloric foods. In this regard, China is a stark contrast to its Taiwan province which acquired high iron/protein imports at about half the level of the mainland. Why is China different from the other Asian fisheries? First, China reduced tariffs on agricultural imports in 2004, making it the freest trading partner in the world. Soy is the high protein food that China imports at higher levels than any other, but it is important to emphasize that this plant protein is being substituted for large quantities of much healthier fishery commodities that are exported. Second, China utilizes its economic position in the region to acquire the most nutritious fishery commodities from high-hunger Asian fisheries to which it exports lower-quality frozen and canned finfish (Ji-Kun et al. 2017). Third, China is the only Asian fishery with a mandated national food and nutrition program that places constraints on imports to keep them in line with food security targets. This point of difference brings us to an important point about the minimal back seat role that the Asian fisheries play with respect to national food security.

We have been describing national food import budgets in a way that might mislead readers to think that Asian states make the decisions about what is imported. However, the reality of the world food system makes the pro-market idealism of the World Food Summit (1996) seem ridiculously naive. The rhetoric of the Summit policies assigns to consumers a great deal more agency than they actually have in the food importing process, and it pretends that states will research, plan and advocate the imports most needed to address nutritional needs. In reality, transnational corporations and domestic capitalists select the imports they are convinced will be most profitable, and they often create new local demand for faddish foods and beverages from rich countries (McMichael 2005). Moreover, international trade policies constrain national governments from setting standards that might interfere with free trade (SAPRIN 2002), so states do not regulate food importing with an eye to domestic nutritional needs. Examination of Table 7 and trade data make it clear that private sector importers selected commodities around two opposing goals: (a) cheap less nutritious foods for the poor and (b) more expensive candies, desserts, liquors, beverages, high-fat snacks, and processed convenience foods for middle class and affluent households. In both cases, the outcome is introduction of higher levels of carbohydrates, sugars and fats that not only fail to address nutritional shortfalls but also cause rising levels of obesity (Ng et al. 2014).

TABLE 7

Nutritional unequal exchanges embodied in trade of Asian fishery commodities, 2016

Part A. Lost both Iron and Protein
Asian fishery MG iron per exported ton MG iron per imported ton Percentage gain or (loss) of iron per imported ton Grams protein per exported ton Grams protein per imported ton Percentage gain or (loss) of protein per imported ton
A aBangladesh 59,151 15,480 (73.8) 261,601 229,040 (12.5)
A aCambodia 59,150 10,180 (82.8) 261,600 239,640 (8.4)
M China-Mainland 30,095 14,070 (53.2) 279,480 231,860 (17.1)
A aIndia 52,650 11,180 (78.8) 265,600 237,640 (10.5)
S aIndonesia 40,365 11,660 (71.1) 273,160 236,840 (13.3)
M Malaysia 35,035 13,980 (60.1) 276,440 232,040 (16.1)
S Myanmar 32,110 24,460 (23.8) 278,240 211,081 (24.1)
S aNorth Korea 73,385 17,380 (76.3) 252,840 225,240 (10.9)
A aPakistan 23,010 10,054 (56.3) 283,840 239,892 (15.5)
S aPhilippines 32,556 12,240 (62.4) 277,999 235,520 (15.3)
S aSri Lanka 32,786 10,360 (68.4) 277,824 239,280 (13.9)
M Thailand 40,625 12,320 (69.7) 273,000 235,360 (13.8)
S Vietnam 32,955 13,840 (58.0) 277,720 232,320 (16.3)
Part B. Gained both Iron and Protein
L China-Taiwan 18,922 39,388 108.2 182,245 223,999 22.9
L Japan 24,504 32,008 30.6 232,920 278,303 19.5
L South Korea 27,488 32,983 20.0 231,145 277,703 20.1

low income food deficient country (FAO 2011a).

NOTES AND SOURCES: MT OF EXPORTS AND IMPORTS WERE AGGREGATED FROM GLOBAL FISHERY ND AQUACULTURE DATABASES, FAO (SEE TABLE 3), THEN CONVERTED TO GRAMS (1MILLION GRAMS PER MT). THE FIGIS DATABASE PROVIDES DETAILED INFORMATION ABOUT SPECIES THAT WERE TRADED. FOR NUTRITIONAL CONTENT OF FISHERY COMMODITIES, WE CONSULTED THE USDA FOOD COMPOSITION DATABASE. NUTRITIONAL VALUES WERE CALCULATED FOR 100 GRAM SERVINGS FOR EACH TRADED SPECIES. THE LETTERS BEFORE NAMES REFER TO THEIR 2010 GLOBAL HUNGER INDEXES (CONCERN WORLDWIDE 2010); A = ALARMING, S = SERIOUS, M = MODERATE, L = LOW

4.2 Nutritional Unequal Exchanges through Food Exports and Imports

If we apply the recent notion of nutritional footprint (Speck et al. 2013), we see that the countries that are characterized by a diet that has both calorie content and nutrient density are the richer countries to which these Asian fisheries export their high iron and high protein foods. While those countries exhibit a high nutritional footprint, the Asian fisheries (except Japan) have a low nutritional footprint because a large segment of their populations consume foods with caloric content that are lacking in nutrient density. In short, the low nutritional footprint of these low to middle income Asian fisheries is associated with negative health outcomes for a sizeable segment of their citizens. Developing countries, like these fishery exporters, are characterized by undernutrition, insufficient proteins and health problems tied to shortfalls in micronutrients, especially iron. These conceptualizations lead us to explore whether these Asian fisheries trade up nutritionally in order to acquire crucial imports that will address domestic malnutrition problems.

The UN COMTRADE statistical database provides data for 425 finfish, shellfish and mollusk species, identifying those intended for human consumption. Of this list, 253 finfish can be classified as nearly pure protein, and most of the crustaceans and mollusks are high in iron. The database lists separately those shellfish that are exported for human consumption, separating them into crustacean and mollusk species.16 Using the Trade Map database of the International Trade Centre, we acquired the quantities of the species of seafoods that were exported and imported by each of the Asian fisheries. Then we used four medical websites to classify those species in terms of their iron and protein content. Exported from Asian fisheries, tuna is the captured fish that is highest in protein while tilapia is the highest protein aquaculture species. In addition, Asian fisheries supply to the world nearly three-quarters of the seafoods that are highest in iron.17 As Figure 6 shows, the most frequently traded high-iron Asian seafood species are mollusks (clams, octopus, blue mullet, oyster) and crustaceans (prawn/shrimp, crab). However, caviar (fish eggs) and two types of high-iron finfish (sardines, anchovy) are routinely exported. In the face of high levels of domestic anemia and protein shortfalls, these Asian seafoods provide from 2.45 to 23.77 milligrams of iron per three ounce serving to distant healthier consumers.

FIGURE 6
FIGURE 6

Nutritional content of frequently traded asian fishery and agricultural commodities

SOURCE: UNITED STATES DEPARTMENT OF AGRICULTURE FOOD COMPOSITION DATABASE, HTTPS://NDB.NAL.NSDA.GOV/NUTRIENTS/INDEX (ACCESSED 7 AUG. 2021)

Since iron deficiency anemia and protein shortfalls are so problematic in the Asian fisheries (see Table 2), we are particularly interested in assessing how well they do in securing high iron and high protein foods through international trade. To analyze these trends, we classified traded foods by nutritional value in order to measure the degree to which crucial nutrients were lost through exports but regained through imports (see Figure 6). Table 5 points to the nutritional unequal exchange that results for these Asian fisheries with respect to export and import of high iron/protein fishery and agricultural commodities that are intended for human consumption. Most of them prioritized the export of fishery commodities over the need for domestic consumption of these seafoods. The thirteen Asian fisheries with moderate to alarming hunger indexes engaged in nutritional unequal exchanges by trading high iron/high protein fishery commodities for less nutritious fish. In contrast, the three Asian fisheries with low hunger indexes traded up nutritionally by exchanging low iron/low protein finfish for high iron/high protein mollusks, shellfish and finfish imported from their Asian neighbors.

Several scholars (e.g., Grote et al. 2005; Spiess 2014) have called attention to the hidden soil nutrients and water that are embodied in exported food crops, and these are ecological unequal exchanges that drain resources inequitably from developing countries. For example, Pengue (2005) estimates that 2002–2003 soybean exports resulted in the extraction of more than 1.2 million tons of nitrogen and phosphorus from Argentinian soils. However, exports also drain food resources from the human populations who produce them (Wimberley and Bello 1992; Wilkinson 2010; Milhalache-O’Keef and Li 2011; Austin et al. 2012). Falconi et al. (2017) have called attention to the caloric unequal exchanges involved in international trade, but they focus on the quantity and economic value of exports versus imports and on hidden ecological costs, not on the actual caloric value of the traded commodities. Since the philosophy of the FAO and international development agencies is that food importing is an important strategy for solving world hunger and malnutrition, we must move beyond using weak proxies for human consumption, like trade value. On the one hand, scholarship about loss of natural resources through exporting identifies externalized ecological costs, not hunger or malnutrition. On the other hand, a focus on the caloric content of traded commodities will conceal the double burden of undernutrition and rising obesity (Kennedy et al. 2004) that now characterizes most developing countries. Indeed, thirteen of the Asian fisheries expend their import budgets in such a way that the caloric content is primarily in unhealthy fats, sugars and carbohydrates (see Table 6), thereby failing to address major nutritional shortfalls that lead to domestic anemia, childhood stunting and other organic diseases. In order to assess whether importing actually addresses nutritional shortfalls, we need to examine trade exchanges in terms of the nutrients that are embedded in the food commodities that are exported and imported. For that reason, Table 7 compares the iron and protein exchanges that occur in the exporting and importing of fishery commodities.

Do the Asian fisheries acquire or lose high iron and high protein fishery commodities through importing? On average, these high fishery exporters shipped out nearly four times more high-iron foods than they imported. It is not surprising that those with alarming hunger indexes exhibit the greatest degree of nutritional unequal exchange and the lowest nutritional footprints. Despite alarming hunger indexes, Bangladesh, Cambodia, India, and Pakistan exported 4.1 times more high iron fishery commodities than they imported. The six fisheries ranked with serious hunger indexes exported 2.7 times more high iron fish than they imported while those ranked moderate shipped out 2.6 times more high iron foods than they acquired. With respect to high iron fishery commodities, it is clear that thirteen of the Asian fisheries are trading down nutritionally. On the world market, the foods that lead to a high nutritional footprint are higher value, reflecting the demand of rich countries. Consequently, the lower nutritional footprints result from the export of high value, nutrient rich foods coupled with the import of lower value, less nutritious higher calorie carbohydrates, sugars, and high fats (see Table 6). In sharp contrast, the three Asian fisheries with low hunger indexes (Japan, South Korea, Taiwan) imported 1.5 times more high iron fish than they exported, and 1.2 times more high protein foods than they lost. Overall, the low-hunger Asian fisheries are trading up nutritionally by importing from Asian neighbors with far worse hunger problems.

What do these numbers mean to individual Asians? When the unequal nutritional exchange is calculated as surpluses or deficits per capita, all these fisheries except Japan are made less food secure through trade. With their alarming hunger indexes, Bangladesh, India, and Pakistan lost about one kilogram per capita of high iron foods. Those judged to have serious hunger problems exhibited per capita deficits of 1.3 to 5.3 kilograms of high iron foods. Among those with a moderate hunger index, China lost nearly three kilograms of iron per capita while Thailand and Malaysia were shortchanged 37 to 47 kilograms per capita. In addition, thirteen of these fisheries experienced per capita protein shortfalls while another three barely met national consumption needs. China achieved a per capita protein surplus of nearly 41 kilograms, much of which was derived from dependency on imported soy that is being substituted for the more nutritious fishery commodities that the Chinese export.

The human benefit of unequal nutritional exchange is evidenced in the polarization between Japan, Taiwan and South Korea and their neighboring fishery exporters. While they receive high iron and high protein foods and fishery commodities from Asian neighbors whose exports sustain their high nutritional footprint, they export to them lower-quality canned fish and processed foods which exacerbate their low nutritional footprints that lack nutrient density.18 In short, these three Asian fisheries eat more than an equitable share of the high iron and high protein commodities produced in this region while a high proportion of the residents of the fisheries that supply them have access to so little of these foods that they exhibit higher incidence of hunger and nutritional deficiencies.

4.3 Do Farm Outputs Offset Fishery Nutritional Shortfalls Caused by Exporting?

In order to determine what foods the Asian fisheries need to import to overcome those nutritional shortfalls, we must examine their agricultural production patterns. When we sort crops into nutritional categories, we see that foods that are high in carbohydrates, sugars and fats account for one-half to three-quarters of crop production in all the Asian fisheries. Consequently, agricultural production does not alleviate the losses of iron and protein caused by fishery exporting (see Table 7). On the one hand, food crops account for a minority of total agricultural production (see Table 4). On the other hand, high iron/protein foods represent a minuscule amount of farm output. Pulses, chicken, meats, eggs, milk, nuts, mangoes and spinach were the only high iron/protein outputs they produced. Because they exhibit protein inadequacies and high incidence of iron deficiency anemia, fisheries with alarming or serious food indexes need to generate more of these nutrients through agricultural production. However, that is not occurring. High iron/protein foods accounted for less than one percent of agricultural production in Indonesia, North Korea, the Philippines, Sri Lanka, and Vietnam, compared to two to four percent in Bangladesh and Myanmar. Pakistan stood out as an anomaly, as it allocated 14 percent of agricultural output to these nutrients. Among the fisheries with moderate and low hunger indexes, high iron/protein foods accounted for less than one-tenth of one percent of agricultural production in Malaysia and Thailand, compared to four to seven percent in Japan and South Korea.19

Throughout the Asian fisheries, there is a nutritional shift to a high beef diet by middle class and elite households which is driving conversion of croplands to pastures for livestock production (Wilkinson 2010). This trend led us to question whether the nutritional impacts of fishery exports were offset by domestic meat production. On the one hand, none of these Asian fisheries is producing enough beef to feed its entire population, so red meat consumption is still a luxury food for the minority who can afford it. On the other hand, the populations of fourteen of the Asian fisheries experience a moderate to severe incidence of anemia that could be offset by access to affordable high iron fishery or beef outputs (see Table 8). On average in 2016, however, the ten Asian fisheries with a high to severe incidence of anemia exported 8.4 milligrams of fishery-iron per capita to every milligram of beef-iron generated domestically. With a moderate incidence of anemia, Malaysia and Thailand e4xported 38 milligrams per capita of iron-rich fishery commodities to every milligram of domestic beef.

TABLE 8

Can domestic meat production offset iron losses from fishery exporting? 2016

Part A. Asian fisheries with severe incidence of iron deficiency anemia
Asian fishery MG iron per capita in exported fishery products MG iron per capita in domestic beef production (after wastage and exports are deducted)
A Bangladesh 26.1 2.0
A aCambodia 99.4 32.8
A aIndia 41.0 19.5
S aIndonesia 129.6 20.8
S Myanmar 194.4 141.0
Part B. Asian fisheries with high incidence of iron deficiency anemia
S a North Korea 170.8 11.7
A aPakistan 15.7 91.8
S aPhilippines 81.9 28.4
S aSri Lanka 28.0 10.6
S Vietnam 512.4 34.7
Part C. Asian fisheries with moderate incidence of iron deficiency anemia
M China-Mainland 90.5 71.5
M Malaysia 283.4 12.6
L South Korea 263.9 43.4
M Thailand 807.1 15.0
Part D. Asian fisheries with mild incidence of iron deficiency anemia
L China-Taiwan 548.5 1.7
L Japan 97.5 29.5

low-income food-deficient countries (FAO 2011a). The letters before names indicate Global Hunger Indexes (Concern Worldwide 2010); A = alarming, S = serious, M = moderate, L = low.

SOURCE: COLUMN 1 WAS CALCULATED USING DATA IN TABLES 3 AND 5. MT OF MEAT WERE AGGREGATED FROM FAOSTAT, THEN WASTAGE AND EXPORTS WERE DEDUCTED. FOR PER CAPITA ANALYSES, THE MT AVAILABLE FOR DOMESTIC CONSUMPTION WERE CONVERTED TO MILLIGRAMS. NUTRITIONAL VALUES WERE CALCULATED FOR 100 GRAM SERVINGS. FOR NUTRITIONAL CONTENT OF MEATS AND FISH, WE CONSULTED THE USDA FOOD COMPOSITION DATABASE. INCIDENCE OF ANEMIA FROM TABLE 2

There are four exceptions to these trends, indicating more extensive reallocation of agricultural lands to cattle pasturage. With a high incidence of anemia, Pakistan produces 5.8 milligrams per capita of beef-iron to every exported milligram of fishery-iron. However, the country’s anemia incidence would be lower if these meat outputs were actually accessible to the poor and much of the middle class. In this context, it is questionable that Pakistan should be exporting its high-iron fishery products. With a moderate incidence of anemia, China exports 1.3 fishery iron milligrams per capita to every milligram of domestic beef. Also exhibiting a moderate anemia incidence, South Korea exports 6.1 fishery-iron milligrams per capita to every domestic beef milligram. With a low incidence of anemia, Taiwan exports 322.6 milligrams of fishery-iron per capita and Japan exports 3.3 fishery-iron milligrams per capita to every milligram of domestic beef-iron. These trends are problematic for two reasons. First, they represent reallocation of farm lands to the production of livestock, limiting the acreage available for production of plant-based high iron/protein foods that are more affordable locally. Second, they indicate a shift toward the western pattern of consumption of less healthy red meats. Third, beef is so expensive in all the Asian fisheries that it is rarely eaten by a majority of the people. Consequently, anemia reaches into both poor and middle class households in the Asian fisheries, including Japan (see Table 2).

4.3 Growing Dependency on Wheat, Soy and Processed Foods

Analysts continue to assume that rice is the central staple of Asian diets, but this has not been a correct assessment for some time. In reality, rice now accounts for 20 percent less of Asian food consumption than it did in 1961 (see Figure 7). By 2010, rice accounted for 28 percent of total agricultural tons produced in Bangladesh and one-fifth of crop output in Myanmar. However, rice did not predominate in any of these fisheries. Indeed, rice accounted for only 5 to 11 percent of total agricultural output in India, Japan, Pakistan and South Korea, one to three 3 percent in China, Indonesia, North Korea, the Philippines, and Vietnam, and less than one percent in Malaysia, Thailand and Sri Lanka.20 While national governments still define rice to be the staple for the poor, the growing Asian middle classes are diversifying their diets toward wheat (FAO 2013), as food importing trends reflect. In 2010, all the major Asian fishery exporters, except the Philippines, spent more of their food import budgets on wheat than on rice. By 2013, however, even the Philippines was importing greater levels of wheat than rice. Indeed, China is now the only country that ranks among the world’s top ten rice importers while the Philippines has slid down to 36th position.21 Even though several of these fisheries (e.g., Bangladesh, the Philippines, Thailand, Vietnam) produce high levels of rice, they also import large quantities of wheat. Indonesia (1st), Japan (3rd), China (6th), South Korea (7th) rank among the world’s top ten largest wheat importers. Even though China and India are now the first and second largest wheat producers in the world, neither country cultivates enough to meet national demand, so both rely on imports.22

FIGURE 7
FIGURE 7

Percentage of rice in total food consumptions, 1990–2009

SOURCE: ADB (2012)

Why is this trend toward dependency on wheat imports significant to the food security of the Asian fisheries? First, wheat is more expensive than rice, so it is not affordable for the poor. Moreover, it has been characterized by price volatility. Between 2002 and 2012, the price index for wheat rose more than the price index for all foods (FAOSTAT). Second, most of these Asian fisheries expend more of their food import budgets on wheat than on high iron/protein foods. India and China are able to expend a great deal more on proteins because they produce much of their national wheat consumption. Thailand, Japan and South Korea expended more on proteins, but they exchanged high iron/protein fishery exports for wheat. Nine of the fisheries with alarming and serious hunger indexes expended more of their food import budgets on wheat than on proteins. Even though rice accounted for more than half of the total crop production in these two countries, low-income food-deficient Bangladesh spent 9.5 times more on wheat than proteins while Myanmar (with a serious hunger index) expended a minuscule amount on proteins compared to wheat (FAOSTAT). What all these fisheries have in common is that they are trading down nutritionally. They export high iron foods in order to acquire foods which have high caloric value but provide very low levels of important nutrients. In the case of wheat, they engage in a nutritional unequal exchange, i.e., high iron/protein foods and fishery commodities into the world market in exchange for a food that is primarily carbohydrate.

Asian traditional diets have not only shifted with respect to cereals but also in terms of growing dependency on soya imports as substitutes for protein/iron exports. China and India are the fourth and fifth largest producers of soya in the world, but they utilize their production nationally. Consequently, these Asian fisheries import most of their soya from the USA, South America and Canada.23 In 2010, soybeans accounted for a majority of the protein imported by Indonesia, North Korea and China while Japan, Malaysia, South Korea, Thailand, and Vietnam utilized two-fifths to half of their protein expenditures on soya imports. About one-quarter of the protein imports of Bangladesh and Myanmar were soybeans while 12 percent of the protein imported by the Philippines was soya.

There are four problems with this pattern. First, prices of soya have risen as world demand has risen; soya cost three times more in 2012 than in 2002. Second, import of soy represents a nutritional unequal exchange of high iron exports for protein imports in fisheries that have high incidence of iron deficiency anemia (see Table 1). Third, these fisheries are substituting dependency on a single protein for production of traditional foods that supplied protein diversity. Fourth, western medical and nutrition experts have documented nutritional dangers of soy for three decades, even though soy is now a fad food around which all kinds of positive advertising claims are made. The soybean contains large quantities of natural toxins that block enzymes needed for protein digestion and iron absorption. Thus, individuals with iron deficiency or those at high risk of developing iron deficiency (which is a serious health problem in these Asian fisheries, especially for women and children) should avoid eating soy. Clearly, soya importing represents a nutritional unequal exchange because high iron exports are exchanged for a protein that has the capacity to lower iron absorption from the few sources that are still available to Asian consumers (Latunde-Dada and Neale 1986). To complicate matters, the processing of soybeans at high temperatures denature them so that much of the nutritional effect of their proteins is dissipated. In addition, soybeans have a much higher degree of contamination by pesticides than most foods (Morck et al. 1982).

There is another trend that indicates the disjuncture between national nutritional needs and food imports. Health and nutrition experts argue that food importing is popularizing globally the worst nutritional habits of westerners, leading toward a rising incidence of lifestyle diseases that once characterized only a few rich countries. Many of the emerging Asian nutritional and health problems are related to the displacement of local fresh fish, vegetables and fruits by imported processed foods that are loaded with high levels of carbohydrates, fats, and sugars (Goryakinab et al. 2015). On average, Asian fisheries with alarming and severe hunger indexes imported 2.5 times more tons of less nutritious processed commodities than high iron/protein foods. With the exception of Malaysia, the fisheries with moderate and low hunger indexes exhibited the opposite pattern. On average, they imported 2.5 tons of high iron/protein foods to every ton of processed foods. However, all the Asian fisheries exchanged fishery products for processed foods. Specifically, these fisheries exported fresh/frozen fish and shellfish of higher nutritional and market value, but they imported fish preparations with carbohydrate and fat fillers and canned fish species of lower nutritional and market value. Indeed, 39 percent of the imports of fish by these Asian fisheries originate from the processing and re-export of their exports by developed countries (FAO 2012b: 41, 70). Philippine scholar Renato Constantino (1988) called attention to this nutritional unequal exchange three decades ago. Protein imperialism results, he argued, from international trade in which richer countries export their high-fat, high-sugar, low-protein foods to poor countries from which they import more nutritious proteins. Moreover, processed foods are linked to the rising obesity among the poor and middle classes in the Asian fisheries (Ng et al. 2014).

4.4 Imported Production Inputs for Export Commodities

These nutritional unequal exchanges are exacerbated by another import pattern. To support their production of crops and fish for export, all the Asian fisheries import fossil fuels, agricultural machinery, boats and tools, animal and aquaculture feeds, fertilizers, pesticides, and live species for propagation. North Korea spends nearly as much on these inputs as it receives for its food exports, while China expends three-fifths of the value of its food exports on imported inputs. India, Vietnam and Thailand lose about one-quarter of the value of food exports in this manner while Indonesia, Malaysia, Myanmar and Sri Lanka allocate 15 to 20 percent of the value of food exports to cover these costs.24 Rather than purchasing high iron/protein foods, Asian fisheries with severe nutritional shortfalls utilize import dollars to acquire inputs to produce exports. In other words, pesticides for exports are prioritized over domestic consumption. The situation of Bangladesh underscores this dilemma. This low-income food-deficient country expends nearly twice as much on imported production inputs as it receives for its food exports. The Asian fisheries make another import choice that has food security implications. On average, the low-income food-deficient fisheries expend $7.80 on petroleum to every dollar utilized for food imports. For instance, India’s food imports cost only 13 percent of what the country pays out for petroleum.25

Table 9 makes clear the nutritional impacts of the food versus feed import choices by the Asian fisheries. In 2016, imports per capita of high iron foods exceeded per capita feed imports in only five of the fisheries. In those countries, however, imports of aquaculture feeds– primarily to produce shellfish exports– cost $1.95 to every dollar’s worth of high iron fish imports for humans. This is why fishers in the Philippines, India and Bangladesh report that fishponds are more nutritious than their household diets (Environmental Justice Foundation 2003). The ten fisheries with high or severe incidence of anemia expended $1.41 per capita of feeds for livestock and fishponds to every import dollar for high iron foods. The four fisheries with moderate incidence of anemia imported $1.16 per capita in feed to every dollar per capita of imported high iron foods. Import patterns help to explain why Japan and Taiwan are the only two Asian fisheries with a mild incidence of anemia. While Japan allocates 1.3 times more per capita to import feeds, Taiwan nearly breaks even in its feed/food imports. It is in the import of high iron fish that Japan and Taiwan stand out from the other fisheries. Japan spent $3.96 on imported high iron fish to every aquaculture feed dollar while Taiwan utilizes only 44 cents for feed imports to every dollar of high iron fish imports. Japan and Taiwan achieve their high iron food imports through nutritional unequal exchanges with hungrier neighboring fisheries (see Table 5). With a moderate incidence of anemia, China spends $8.90 on imported aquaculture feeds to every dollar utilized to import high iron fish for human consumption. China acquires those aquaculture feeds by importing small fish from neighboring hungrier fisheries that should utilize those exports as human high protein foods.

TABLE 9

Food versus feed in the import budget, 2016

Part A. Asian fisheries in which feed imports exceed high-iron food imports
Asian fishery Incidence of anemia Thousand $US spent on high iron human foods (excludes fish) Thousand $US spent on high iron fish imports for humans Total thousand $US spent on foods & fish for humans Thousand $US spent on livestock feeds Thousand $US spent on fish feeds Total thousand $US spent on livestock & fish feeds $US spent per capita on high iron foods $US spent per capita on feeds
aCambodia Severe 67,514 1,449 68,963 129,845 3,976 133,821 4.36 8.46
China-Mainland Moderate 13,805,343 515,552 14,320,895 25,679,914 4,585,575 30,265,489 10.54 22.27
China-Taiwan Mild 1,710,173 1,090,976 2,801,149 2,419,197 480,062 2,899,259 118.91 123.08
aIndonesia Severe 3,286,338 82,273 3,368,611 4,025,444 208,529 4,233,973 12.93 16.25
Japan Mild 2,569,624 5,146,965 7,716,589 8,983,298 1,299,079 10,282,377 61.08 81.40
Malaysia Moderate 981,354 307,599 1,288,953 2,298,941 258,911 2,557,852 41.91 83.18
aNorth Korea High 80,279 30,453 110,372 262,271 47,228 309,499 4.36 12.24
aPakistan High 336,076 63 336,139 541,006 33,373 574,379 1.74 29.79
South Korea Moderate 3,275,215 1,986,003 5,261,218 5,676,502 706,351 6,382,853 104.17 126.38
Thailand Moderate 1,511,133 612,040 2,123,173 2,920,079 21,024 2,941,103 31.15 43.16
Vietnam High 1,585,225 482,502 2,067,727 6,209,570 223,129 6,432,699 21.89 68.11
Part B. Asian fisheries in which total high-iron food imports exceed total feed imports but fish feed exceeds human fish imports
aBangladesh Severe 1,370,769 60,297 1,431,066 884,700 89,004 973,704 8.78 5.80
aIndia Severe 2,257,772 17,523 2,275,295 543,976 43,840 587,816 1.71 0.44
Myanmar Severe 234,080 8,738 242,817 178,833 10,782 189,615 4.47 3.49
aPhilippines High 1,529,041 56,939 1,585,980 401,006 121,092 522,098 15.51 5.11
aSri Lanka High 759,731 2,985 762,716 163,377 21,024 184,401 36.65 8.86

low income food deficit countries (FAO 2011a).

SOURCES AND NOTES: ANALYSIS OF DATA AGGREGATED FROM GLOBAL FISHERY AND AQUACULTURE DATABASES, FAO AND FAOSTAT DATABASES. INCIDENCE OF ANEMIA FROM TABLE 2

TABLE 10

Nonfood production, 2016

Fishery territory Total MT agricultural production MT nonfood crops (% total) Nonfoods produced Foods converted to nonfoods for export
A aBangladesh 176,180 105,629

(60.0)
Tea, Rubber, Tobacco, Jute, Floricultural
A aIndia 2,832,574 1,939,976

(68.5)
Tea, Coffee, Rubber, Tobacco, Jute, Cotton, Cottonseed, Floricultural Fish, Seaweed
A aPakistan 264,181 119,582

(45.3)
Cottonseed, Rubber Fish, Coconut Oil
S aIndonesia 4,873,900 3,651,544

(74.9)
Rubber, Tobacco, Coffee, Tea, Jute Fish, Coconut Oil, Palm Oil, Seaweed
S Myanmar 173,806 111,805

(64.3)
Rubber, Tobacco, Coffee, Tea, Cotton, Jute Coconut Oil
S aNorth Korea 75,176 63,000

(83.8)
Tobacco, Rubber, Tea, Coffee Fish, Seaweed
S aPhilippines 585,569 519,866

(88.7)
Tobacco, Rubber, Coffee, Floricultural Fish, Coconut Oil, Palm Oil, Seaweed
S aSri Lanka 459,589 434,636

(94.6)
Tobacco, Rubber, Coffee, Floricultural Coconut Oil, Palm Oil, Seaweed
S Vietnam 1,956,988 1,867,512

(95.4)
Tobacco, Rubber, Tea, Coffee, Floricultural, Jute Fish, Coconut Oil, Palm Oil, Seaweed
M China-Mainland 6,386,474 4,911,974

(76.9)
Tobacco, Rubber, Tea, Coffee, Floricultural, Jute, Cotton Fish, Coconut Oil, Palm Oil, Seaweed
M Malaysia 953,300 908,829

(95.3)
Tobacco, Rubber, Tea, Coffee Fish, Coconut Oil, Palm Oil
M Thailand 3,294,636 3,274,786

(99.4)
Tobacco, Rubber, Tea, Coffee, Jute, Floricultural Fish, Coconut Oil, Palm Oil, Seaweed
L Japan 170,783 122,600

(71.8)
Tea, Tobacco Fish, Seaweed
L South Korea 65,244 37,050

(56.8)
Floricultural Fish, Seaweed

low-income food-deficient country (FAO 2011a). The letters before names indicate Global Hunger Indexes (Concern Worldwide 2010); A = alarming, S = serious, M = moderate, L = low. Data not available for Cambodia and Taiwan.

SOURCE: ANALYSIS OF DATA AGGREGATED FROM FAOSTAT AND GLOBAL FISHERY AND AQUACULTURE DATABASES, FAO, DATABASES. TEA AND COFFEE ARE CLASSIFIED AS NONFOODS BECAUSE THEY HAVE NO CALORIC VALUE

4.5 Impacts of Food Imports on Agricultural Production

As Figure 8 shows, food imports expanded dramatically in the Asian fisheries between 2001 and 2011. Imports more than quadrupled for countries with alarming hunger indexes while those with serious hunger indexes more than doubled their imports over this decade. What have been the impacts of these rising imports? First, we know from the data about undernutrition that food imports have not offset nutritional shortfalls (see Table 9). Second, food importing has had the effect of dampening Asian agricultural production. The Food and Agriculture Organization (2003c) points out that “high import growth can undermine otherwise viable domestic production.” Since 2000, public spending on agricultural and fishery research and extension systems has stagnated in the Asian fisheries, except China and India (ADB 2013). According to Chang and Shih-Hsun (2011: 10),
FIGURE 8
FIGURE 8

Percentage increase in $US value of food imports in the major Asian fisheries, grouped by global hunger index, 2001–2011

SOURCES AND NOTES: THE VALUE OF ALL CATEGORIES OF FOOD IMPORTS WERE AGGREGATED FOR 2001 AND 2011 FROM UN COMTRADE DATABASE, THEN PERCENTAGE OF GROWTH WAS CALCULATED BETWEEN THESE TWO YEARS. GLOBAL HUNGER INDEXES FROM CONCERN WORLDWIDE (2011)

agriculture is increasingly neglected in most Asian countries. In Japan, agriculture is in a freefall decline. In the years between 1960 and 2005, the share of agricultural output in GDP dropped from 9% to 1%, the food selfsufficiency ratio from 79% to 41%, and agricultural land, indispensable for food security, from 6.09 million hectares to 4.63 million hectares. Meanwhile, the ratio of parttime farm households, which derive more than half their income from nonfarm employment, increased from 32.1% to 61.7%. The percentage of farmers over 65 years old also jumped from 10% to 60%. Gross agricultural output in 2006 was 8.5 trillion yen, less than the sales volume of Panasonic.

For instance, South Korea has opted to prioritize its urbanized industries, showing little interest in agriculture. It now imports a majority of its food, making it very difficult for farmers to earn livelihoods. Its urban centers are symbols of ‘sparkling Korea’ while poverty characterizes the countryside. Since the average farmer is older than fifty and tills a few hectares, the farm sector is stigmatized by most Koreans as backward (Müller 2011).

Though the populations and labor forces of most of the Asian fisheries are still disproportionately rural, they have shown sharp declines in food self-reliance, and the share of the GDP represented by agriculture has shrunk. All the Asian fisheries have undergone a deterioration in agricultural self-reliance since implementation of the 1995 WTO Agreement on Agriculture.26

The deterioration is a reflection of the much higher growth in food imports … because domestic production cannot compete with cheap imports. … Small producers incur large income losses (relative to the retail prices they received in the past) while traders and firms have reaped significant benefits. The impact of the constantly diminishing share of total income accruing to these small producers has been devastating in terms of social dislocation, reduced entitlements, and poverty as well as food insecurity. (GuhaKhasnobis et al. 2007: 282–89)

Imported production inputs for export crops and aquaculture have also impacted small producers negatively.

5 Nonfoods and Asian Food Security

Nonfood agricultural and fishery exports pose serious threats to Asian food security in two ways: (a) use of farmlands to cultivate nonfood export crops and (b) conversion of foods into nonfood uses. The major Asian fishery exporters utilize a growing share of their agricultural lands to cultivate nonfood crops for export, limiting the ecological resources that are left to be used for the production of foods for domestic consumption. All these Asian fisheries produce thousands more tons of nonfoods than of foods that are rich in iron and protein (see Table 4). In addition to feed grain exporting, the nutritional shift to a high animal protein diet by Asian middle classes is driving greater allocation of farm lands to cultivate feed grain (Wilkinson 2010). Since 2000, at least 11 percent of Asian food croplands have been reallocated to nonfoods, including biofuels (Elder and Hayashi 2018). To permit agricultural diversification towards high-value commodities for export, rice and vegetable fields are increasingly being displaced by floriculture, rubber and palm oil production (FAO 2011b; Gray 2008; Ziegler, Fox and Xu 2009). These Asian fisheries produce 82 percent of the world’s rubber, 62 percent of tobacco, 53 percent of cotton (FAO 2010) and more than 90 percent of jute and similar fibers (FAO 2009b). Increasingly, Indonesia and Malaysia are prioritizing palm oil production over food crops (Gellert 2015). In addition, these fisheries generate two edible, noncaloric nonfoods, i.e., more than half the world’s tea and one-quarter of coffee (FAO 2010). To cultivate floricultural exports (primarily cut flowers and potted houseplants), three-quarters of the world’s lands, nearly one million hectares, are concentrated in Bangladesh, India, the Philippines, Sri Lanka, Vietnam, China, Thailand and South Korea.27

As a result of this prioritization of nonfood exports, food crops account for a minority of total agricultural production. On average, nearly 62 percent of the total agricultural production of the countries with alarming hunger indexes is allocated to nonfoods while nonfoods account for nearly 84 percent of agricultural outputs of the countries with serious hunger indexes. Alarmingly, nonfoods comprise 95 percent or more of crop outputs in Sri Lanka, Vietnam, Malaysia and Thailand. Even in Japan, foods account for less than one-quarter of total agricultural output. Pakistan is the only Asian fishery that generates more food than nonfood crops. It is likely that food production is even lower for these countries than Table 4 makes it appear. On the one hand, official agricultural statistics do not report all nonfood crops. For instance, India is using vast areas for jatropha plantations to produce diesel, but this production is not reported in international data (Aziza-Montobbio et al. 2010). On the other hand, it is not possible to disaggregate official statistics so as to separate out the large number of hectares used for production of foods that are being redirected to nonfood uses, especially corn, coconuts and palm oil.

There is a second way in which nonfoods pose serious threats to food security. As part of the unequal nutritional exchange, these Asian fisheries reallocate foods from their domestic human food chains to export them for nonfood uses in richer countries. For instance, they have trapped themselves in what Yotopoulos (1982) terms the food versus feed dilemma. The modern food-feed competition entails an international division of labor in which developing countries produce animal feeds for the richer segment of the world.

Starchy food grains, which double as feed grains, are transformed into costly animal products, resulting in less energy and protein than was contained in the original feed. A kilogram of beef provides 1,140 calories of energy and 226 grams of protein, but the feed grain for producing that kilogram of feed, if directly consumed as food grain … provides as much as 24,150 calories and 700 grams of protein. Demand for costly animal products is heavily concentrated among the well-to-do who thereby draw away grain for use as feed for animals, reducing direct consumption as food for the poor both at a global level and within a given developing country. (Patnaik 2010: 86–87)

In these Asian fisheries, more than half of cereals and 83 percent of coarse grains (barley, oats, rye, sorghum) are diverted into feeds (Chand 2008; FAO 2013a). Throughout Asia, cassava is the third most important source of calories in the human food chain. While production of this tuber has expanded 3 percent annually since the 1970s, much of this output has been exported to be used in livestock and poultry feeds globally (Prakash 2010).

In 2010, these Asian fisheries produced nearly 89 percent of the world’s supply of palm oil and 88 percent of the coconut oil, exporting most of it to be used for biofuels and industrial purposes.28 While they supply nearly 90 percent of the world’s exports of these two oils, they import (mostly from the US and Europe) nearly one-fifth of the world’s traded edible oils, in an attempt to meet the domestic shortfall of this type of food. The Food and Agriculture Organization (2008a) points to negative impacts of biofuels on world food security, especially for countries that divert domestically consumed foods to nonfood exports. These Asian fisheries are diverting palm oil, coconut oil, and corn into exports to be processed into biofuels (Chand 2008). In Vietnam, the oil of some fishery species is used for biodiesel (Philippine Annual Fisheries Profile 2007).

Even in the face of national shortfalls of seafoods, these Asian fisheries divert outputs into nonfood uses. Indeed, they export nearly 17 percent of their fishery production as nonfoods, such as aquarium specimens, fish meal to be used in livestock and aquaculture feeds, pet foods or fertilizers. In addition, sea plants are removed from local food chains to be exported for industrial and nonfood uses in richer countries. In 2012, China, India, Indonesia, Japan, Malaysia, North Korea, the Philippines, South Korea, Thailand and Vietnam ranked among the world’s top 30 cultivators and exporters of seaweed derivatives. Though a low-value commodity in international markets, seaweed is rich in several nutrients. One cup of seaweed provides 150.4 milligrams of Omega3 fatty acids and nearly 20 grams of protein. It is also a good source of vitamin A, vitamin C, vitamin E, vitamin K, niacin, pantothenic acid and phosphorus, and a very strong source of riboflavin, folate, calcium, iron, magnesium, copper and manganese. However, it has been extracted from traditional Asian diets to become a significant input into commodities produced by rich countries. Seaweed enters the global market in the form of carrageenan, a substance that is used as an additive in many processed foods and for numerous nonfood industrial purposes (SIAP 1996).

6 Will Aquaculture Solve Asian Protein and Iron Shortfalls?

The success of aquaculture is that it has vastly expanded world output of fish and marine foods. The failure and the dilemma of aquaculture, however, is that it has integrated fish and marine resources into global commodity chains, threatening the food security of Southern exporters. Despite all its purported advantages, the Blue Revolution is really food imperialism (Yoshinori 1987). Export-oriented aquaculture has concentrated control over the world’s fish and marine foods into the hands of a few multinational corporations. Rather than eradicating hunger or expanding resources to feed Southern populations, aquaculture has further polarized world food distribution and consumption. Thus, it is highly unlikely that fish farming will insure food security for Southern nations because aquaculture outputs are driven by distant buyer demands, not by the goal of ending hunger in the producing fisheries (McMichael 1998). Despite their own domestic malnutrition problems, many low-income food-deficient countries prioritize the export of seafoods that are central to local consumption (FAO 2012b). On the one hand, industrial aquaculture re-orients local ecological resources from domestic production and monopolizes them to the point that small fishers can no longer generate their livelihoods in those ecosystems. On the other hand, developing countries employ their fishponds, fish cages and pens, and mariculture projects to maximize outputs of export species that are the latest food fads or industrial additives in richer countries.

Because of the global demand for consumption of a range of exotic species, developing countries expended significant amounts in research and development to improve the fishpond yields of those export crops in the 1990s (FAO 1995). For example, technological advances in breeding and nutrition, investment and financial incentives, and rising market demand in the United States, Japan and Europe contributed to the explosive 1990s boom in the Asian shrimp industry (Skladany and Harris 1995). By 2004, shrimp was the primary global aquaculture commodity, accounting for 18 percent of the total value of internationally traded fishery products (FAO 2007). Since 1990, Japan and China have been the two most influential countries in the development of the global aquaculture industry. In most decades since 1975, they have invested more in export-oriented fisheries of Asian and African countries than either the World Bank or the Asian Development Bank. In the fisheries that export those seafoods, however, three-fifths or more of the population can no longer afford to eat these commodities. Even though the World Bank and the IMF advocate shellfish farming as a solution to food security in the Global South, shrimp contributes little to the nutritional needs of the world’s malnourished people because it is primarily marketed as a luxury item that is consumed mainly by the rich in the developed world (Shiva 2000: 43).

Furthermore, agro-industrial fisheries consume more resources than they produce, further threatening food security. In Asia, aquaculture systems require three units of wild fish to every unit of food they produce, generating a net protein loss (Naylor et al. 2001). Moreover, one-quarter of aquaculture production never enters human food chains because it is absorbed as feeds for fish farming or grown as the hatchlings for future crops (CGIAR 1995). Massive amounts of smaller fish and shellfish are fed to carnivorous export species, leaving less natural protein for domestic consumers, especially the rural poor (FAO 2004a; Toufique 2015: 98).

To complicate matters, Asian aquaculture is not sustainable because it is an extractive industry that booms only so long as ecological resources are available and market prices are stable (European Commission 2002). Fish farming projects bust once environmental degradation threatens the supply base or when new competitive producers drive down global prices. According to Harriet Friedmann (2000: 480),

Mobility of capital and labor, global sourcing and marketing, all disrupt the living and material cycles of local ecosystems and then attempt to compensate for the disruptions through more technology, more purchase of inputs, more selling or using of wastes. … Over time, capital movements and markets eliminate the remaining wild places surrounding ecosystems. Thus, ecosystems are relinked through the very social institutions– market and transnational corporations– that disrupt them. Market and industrial techniques are called upon to find ever larger solutions, yet the only place that substances (and models) can be found is in the very earthly cycles needing repair.

Most of the Asian fisheries developed shrimp aquaculture in the 1980s and 1990s but faced serious ecological and economic problems with shellfish farming by 2000 (Mulekom et al. 2006: 551–54). We will explore this boom to bust cycle in Philippine shrimp farming in Chapters 2 to 4.

Because they accumulate feeds, chemicals and waste, fishponds generate unsanitary conditions that cause fishkills and dump high levels of pollution into rivers, coastal waters and farmlands. Unprofitable after five to ten years of intensive farming, fishponds leave behind land and waterways that will be unproductive for several centuries (Skladany and Harris 1995; McGinn 2002). Moreover, agro-industrial aquaculture is capital-intensive, requiring the import of new production technologies and competitive species about every eight to ten years (Skladany and Harris 1995; FAO 2008c). Because exporters must repeatedly innovate to keep up with world market fads, they are pressured to import genetically modified species, feeds, chemicals and technologies (Lebel et al. 2002; FAO 2008d). While ecological degradation and changing world consumption fads account for the bust cycle in fishponds, competition from synthetics and from alternative agricultural commodities (such as corn starch) are much more likely to trigger bust cycles in sea plant exports, such as seaweed (Japan Times 2020). In short, no aquaculture export commodity booms very long in the world market, and it will diminish or destroy natural resources within a decade.

7 Food Security and Pressures toward Depeasantization

Pressures toward Asian depeasantization began in the 1980s with imposition of neoliberal structural adjustment programs that were designed to force indebted Southern countries to integrate their natural resources and their agricultural laborers into the world food trading system (SAPRIN 2002). According to Baviera and Bello (2009: 8), “the right hook of structural adjustment was followed by the left hook of trade liberalization in the context of unequal global trading rules.” By pushing for defunding of government programs, World Bank and IMF policies eroded the productive capacity of peasant agriculture. Early in the 21st century, the World Bank (2018: 138) pointed to the negative impacts of integration of peasant agriculture into the world food system.

Structural adjustment in the 1980s dismantled the elaborate system of public agencies that provided farmers with access to land, credit, insurance inputs, and co-operative organizations. The expectation was that removing the state would free the market for private actors to take over these functions– reducing their costs, improving their quality, and eliminating their regressive bias. Too often, that didn’t happen. … The private sector emerged only slowly and partially– mainly serving commercial farmers but leaving smallholders exposed to extensive market failures, high transaction costs and risks, and service gaps. Incomplete market and institutional gaps imposed huge costs in foregone growth and welfare losses for smallholders, threatening their competitiveness and, in many cases their survival.

To complicate matters, structural adjustment plans mandated the prioritization of “globally high-value” export crops and fishery species (SAPRIN 2002).

In the 21st century, those small Asian farmers and fishers who do not contribute targeted cash crops to export agendas are treated by their own governments like “historical remnants destined to disappear” (Mies and Shiva 2001: 235). In short, agriculture and fisheries are de-localized and production is standardized into a narrow menu of commodities that are in demand globally. In reality, world agriculture has become a transnationalized space in which the control of peasant farmers and fishers over production and distribution is minimized (McMichael 2005: 275–81). Moreover, the global food system disconnects production from consumption and delinks farmers from local markets where they have traditionally disposed of their surpluses. Instead, distant consumer demands for foods determine material relations of food production, diminishing the capacity of peasant farmers and fishers to effect fair prices for their outputs (Friedmann 2000). In Global South communities, accumulation by dispossession (Harvey 2003) operates through structural adjustment strategies to privatize ecological assets and to displace peasant agriculture. Following the restructuring of farm land and fisheries for export, independent farming and fishing are replaced by contract arrangements instituted by traders and agribusinesses, further exacerbating the vulnerabilities of small producers. “Contract farmers bear all the risks related to production and become extremely dependent on demand from the world market” (Delforge 2004: 1). Subsequently, local provisioning is weakened by increased food and fish importing (McMichael 2005: 266).

7.1 Land and Waterway Dispossession

Two of the worst impacts of globalized aquaculture are the dispossession of peasants from their lands and the destruction of traditional livelihoods (Harvey 2003). Throughout the Asian fisheries, the export orientation of fisheries and aquaculture has led to the marginalization of communities that had traditionally been involved in fishing and fish processing (Kurien 2002). A key factor in globalization of fishpond production has been privatization of commons. The first step in this process has been a re-definition of public ecosystems as being “available for development” because they are “idle waste lands that are unproductive.” Following this rationale, governments have transformed hundreds of thousands of public coastal areas into single-purpose private property (Skladany and Harris 1995: 182). Loss of access to these natural resources has threatened the survival of peasant fishers in every Southern country that specializes in export aquaculture (Shiva 2000). Moreover, aquaculture has destroyed small-scale farms and enterprises to pave the way for corporate-owned agribusiness enclaves (Bailey and Skladany 1991). In the global shrimp chain, for instance, small-scale traditional ponds have been aggregated to form larger, export-oriented farms. By controlling land and waterways and by relying on contract farming, larger aquaculture firms vertically integrate activities from production to post-harvest to marketing (Skladany and Harris 1995: 181). Even though peasants comprise a majority of the fishers located in areas where commercial aquaculture is entrenched, these households are marginalized from these economic activities (Bailey 1988b: 36). On the one hand, large aquaculture operations require high capital investments that small entrepreneurs cannot provide (Primavera 1991). On the other hand, large projects monopolize the credit offered by banks and financial institutions (Shiva 2002).

Furthermore, export aquaculture has led to the elimination of employment opportunities for Southern coastal populations. Despite the expensive inputs, export-oriented aquaculture employs far fewer laborers than do small-scale fishing operations. The net result has been that unemployment has risen among fishing households in the Global South that have converted to Blue Revolution production strategies (Shiva 2002). Moreover, few workers are required for the aquaculture systems, and child laborers are often exploited (Bailey and Skladany 1991). Worse, corporate shrimp farming has been tied to murders of peasant fisher-activists in eleven Asian and Latin American countries, including the Philippines (Environmental Justice Foundation 2003: 26).

8 Ecological Degradation of Asian Fisheries and Food Insecurity

More than one-third of global carbon and greenhouse gas emissions are generated by the production, processing and packaging for the world food system, and a majority of those emissions come from agriculture (Crippa et al. 2021a). The ecological costs of food extraction for export have been externalized to Asian fisheries for decades. Export-oriented agriculture is grounded in the systematic externalization of costs to the local environment to maintain productivity that will be consumed by distant consumers. According to Marcus Taylor (2014: 193–94),

Industrial agriculture externalises costs to boost yields in two ways. First, it undercuts the ecological underpinnings needed to produce food– water, soil formation, biodiversity– through excessive use. Second, it is predicated upon the production of side effects– from groundwater contamination, pollution of surface water and greenhouse emissions– that undermine the capacity to generate future yields. Indeed, this model of agriculture deepens the very problems that it argues it is responding to. It is fossil-fuel intensive, produces significant methane emissions from industrial livestock production and nitrous oxide emissions from fertiliser application and promotes major land-use changes through deforestation. In short, modern industrial agriculture appears efficient if we willfully ignore the externalisation of costs that are displaced outward across space and time.

The more developed, less hungry countries to which most of the Asian fisheries export their food and fishery resources benefit from the ghost acres of land and waterways that are embodied in the exported commodities (Borgstrom 1967). Those exports create “phantom carrying capacity” for the importing countries, leaving behind resource depletion and ecological damage (Koellner and Sleen 2011). For example, the European Union (EU) has one of the highest land and fishery footprints in the world. Nearly 60 percent of the land the EU needs to meet demands for agricultural and fishery products derives from developing countries. While European Union land consumption is 1.3 hectares per capita, the Asian fisheries from which it imports foods average less than 0.4 hectares per capita (Friends of the Earth 2011). Similarly , Japan, China, South Korea and Taiwan acquire ghost acres that are embodied in crop and fishery imports from their less hungry neighbors (see Table 5). At the same time that the Asian fisheries are losing so many ghost acres through food and fishery exporting, the arable land available for crop production is rapidly shrinking (see Figure 9).

FIGURE 9
FIGURE 9

Hectares per capita of arable land, 1961–2011

SOURCE: ADB (2013: 41)

Defined in terms of the area of biologically productive land and water needed for production and waste assimilation, the ecological footprints of all the Asian fisheries, except Cambodia, exceeded their natural biocapacities in 2020 (see Figure 10). The ecological footprint of ocean fishing “is much larger than those of other forms of food production, even though capture fisheries supply only 1.2 percent of global caloric for human food consumption. More than half of the world’s oceans are subject to industrialscale harvest, spanning an area four times that covered by terrestrial agriculture” (Kroodsana et al. 2018: 906). By the mid-1990s, a third of the world’s oceans and two-thirds of continental shelves (primarily where small-scale fishing occurs) had an ecological footprint of 1.10. There is a startling contrast between the resource exploitation rates of agriculture and fishing.

FIGURE 10
FIGURE 10

Biocapacity and ecological footprint of the major Asian fisheries, 2020

SOURCE: WORLD POPULATION REVIEW (2021)

Doubling of world agricultural production from 1961 to 1995 was accompanied by an increase of only 10% of the surface under cultivation. Over the same period, marine fisheries, which underwent a comparable 2.4 fold increase in catch … required a nearly 4fold increase in exploited area. (Swartz et al. 2010)

What is the ecological state of the Asian fisheries as a result of their exporting and overextension of natural resources? By 2009, 20 percent of the world’s fishstocks had crashed, 40 percent were over-exploited, and 35 percent were fully exploited (Eggert and Greaker 2009: 2). In 2010, only about 11 percent of world fishstocks were not being fully exploited (FAO 2012b: 58). Nineteen of the world’s 23 commercial tuna fisheries are depleted, endangered or vulnerable to extinction; another nine are fully fished (FAO 2006b). Many of these fishing grounds are located in the oceans and the continental shelves that surround the Asian fisheries. As we move into the 21st century, the ecological crises of Asian fisheries will further threaten regional food security. Because of their high production and export levels, Asian countries have been harder hit environmentally than the global averages. Consequently, Asian fisheries are 60 percent or more over-fished, with many species facing extinction (Hersoug 2004: 21). In addition to stress on coastal waters, overfishing is rampant throughout South Asian near-shore and inland waters. Many freshwater species have been depleted or are extinct, and rivers have been severely degraded (Pomeroy 2012). Moreover, Asian fishery-dependent communities are more vulnerable to the damage caused by climate change (Selvaraju et al. 2011). By 2012, the epicenter of the world fisheries crisis had shifted to the Asian fisheries (Suh and Pomeroy 2020).

Climate change is having significant impacts on the Asian fisheries, as we explore more fully in Chapter 7. Climate variability and change are modifying the migration patterns and productivity of marine and freshwater aquatic species. Marine capture fisheries are affected by rising sea temperature and sealevel rise. In 2016, the World Risk Report ranked thirteen of the Asian fisheries with a high to very high risk of natural disasters (Garschagen, Matthias et al. 2016).29 More drastic weather conditions have increased over the last decade, including intense storms that result in severe calamities to fishing communities along the coastal areas. Moreover, drastic changes in seasonal patterns have been observed in inland areas, including changes in rain and drought periods that alter inland water bodies (SEAFDEC 2017: 144–179).

For the sixteen Asian fisheries, climate change will continue to bring the threats that have begun in the 20th century: rises in sea level, rising temperatures of land, waterways and oceans, rising CO2 levels, increased frequency of natural disasters, alteration of precipitation patterns, and increased frequency of extreme storms and flooding (World Bank 2013b). What will be the impacts of climate change on regional food security?

The changing climate affects food production directly through changes in agroecological conditions, and indirectly by altering income growth and its distribution. … Shifts in land suitability will likely lead to an increase in suitable cropland in higher latitudes and a decline of potential croplands in lower latitudes. Weather is expected to become more variable and volatile, with more frequent and severe extreme events. Fluctuating crop yields and local food supply will make achieving food security more difficult. (ADB 2013: 62)

South Asia– which already exhibits the highest incidence of undernutrition in the world– will experience the highest degree of ecological instability and worsening food insecurity (Islam et al. 2021).

Climate change is likely to reduce yields for irrigated rice by 14 to 20 percent, for irrigated wheat by 32 to 44 percent, and for irrigated maize and soybeans by 2 to 18 percent (Rosegrant et al. 2013). Rises in sea level will cause the worst cropland and fishery impacts in Bangladesh, China, India, Indonesia, the Philippines and Vietnam (Islam et al. 2021). China’s food self-sufficiency is likely to fall (Huang et al. 2017), and its need for increased imports will put added pressure on its neighboring fisheries. By 2050, prices for cereals and soybeans are projected to rise 20 to 70 percent throughout the Asian fisheries, exacerbating the intra-national inequalities among rural and urban communities and between poor and high-income households. Increased prices will bring lower caloric intake, so the number of malnourished children will increase by 2 million in South Asia and by 2.8 million in East Asia (ADB 2013: 65–66).

In the 21st century, illegal cross-border fishing has triggered ecological battle lines among the Asian fisheries (Williams 2013). Ecological changes are pushing China’s massive fishing fleet far from home waters. China has lost half its coastal wetlands, 57 percent of its mangroves, and 80 percent of its coral reefs (Cao et al. 2017).Tensions between China, the Philippines, Japan, North Korea, South Korea, Indonesia, Vietnam and Malaysia have made international news (Park et al. 2020; Wilcox et al. 2021). In October 2020, ASEAN member states established a network for monitoring and surveillance of illegal cross-border fishing. In March 2021, China announced its launch of nine law enforcement actions, including a fishing ban in the Yangtze River, aquatic wildlife protection, the suspension of ocean fishing in summer, and proper use of inputs for aquaculture (Cao et al. 2017).

9 Intra-national Inequalities in Food Access

Joan Robinson (1979: 57) contends that “inequality of distribution is the main cause of the existence of large numbers of people who are unable to satisfy the need for even a minimum standard of nourishment.” The first major level of inequitable food distribution occurs through trade commodity chains within the world food system. Previously, we have pointed to the food drains from hungry Asian fisheries to regions of the world that are not hungry (see Table 5). We have described the inequitable global distribution of iron and protein from the Asian fisheries to regions of the world that utilize those foods as luxuries, not as essential survival requirements (see Table 6). We have also demonstrated that these Asian fisheries export high-iron and high-protein fishery commodities in exchange for less nutritious imports (see Table 8) that are causing a double burden of malnutrition in the Asian fisheries. Transformation of foods into nonfoods for export and to feed export livestock and aquaculture species have been prioritized over human consumption, driving up local prices and impacting poor households the worst (see Tables 3 and 4). Eleven of the Asian fisheries expend 1.3 to 17 times more to import livestock and aquaculture feeds than to acquire high-iron foods for humans, thereby privileging distribution of limited resources to animals being produced for export (see Table 9) over solving regional nutritional shortfalls.

Measured by the $1.25 a day standard, two-thirds of the world’s poor are concentrated in the sixteen Asian fisheries, three-quarters of them in India and China (ADB 2013). Consequently, the second level of inequitable food distribution occurs nationally. In spite of impressive gains in production, extreme inequities persist within the Asian fisheries (FAO 2005: 3). Despite strong growth in GDP between 2000 and 2010, wealth and income were highly concentrated into the hands of the richest 20 percent while two-fifths to three-quarters of households remained poor (see Table 11). Between 2002 and 2013, food prices remained relatively static and cheaper in richer developed countries while foods were more expensive in the Asian fisheries. Between 2000 and 2010, food prices were not only higher than nonfood prices, they were also more volatile (ADB 2013). Since the Asian poor spend more than half of their household budgets on food, food price increases impact them far more drastically than richer households. Indeed, “a one percent increase in contemporaneous food price inflation leads to a 0.2% increase in infant and child mortality and a 0.4% increase in prevalence of undernourishment” (ADB 2013: XVII). And a majority of that undernourishment and child mortality occur disproportionately among poor rural households. As Table 11 shows, there is considerable inequality in the distribution of food in the Asian fisheries. About one-quarter to one-third of people fall below or above the national per capita intake of food, most getting less than average, some getting more. A major source of inequitable access to food lies in the systemic reliance on bonded and forced labor (discussed more fully in Chapter 8). In India (which has the highest incidence of both bonded labor and hunger among the Asian fisheries), the calorie intake of the poorest quartile is 30 to 50 percent less than the calorie intake of the top quartile of the population.

TABLE 11

Intra-national indicators of inequality that impact access to food

Part A. Ranked low by the United Nations human development index
Fishery territory % average annual GDP growth, 2000–2010 % population in poverty at $2 per day Gini coefficient wealth distribution % income held by highest 20% % poor household budget spent on food
A aBangladesh 5.9 76.5 .66 41.4 65.0
S Myanmar 6.8 NA NA NA NA
S aNorth Korea NA NA NA NA NA
A aPakistan 3.5 60.2 .63 40.0 75.0
Part B. Ranked medium by the United Nations human development index
M China-Mainland 9.1 27.2 .55 47.1 NA
A aIndia 5.0 68.8 .70 42.8 68.0
S aIndonesia 5.7 46.1 .77 46.0 22.0
S aPhilippines 5.3 41.5 .72 49.7 61.0
M Thailand 5.3 41.0 .71 46.7 na
S Vietnam 6.2 43.4 .68 43.4 65.0
Part C. Ranked high by the United Nations human development index
M Malaysia 2.3 NA .73 51.5 NA
S aSri Lanka 6.1 NA NA 44.6 60.0
Part D. Ranked very high by the United Nations human development index
L Japan 0.9 NA .55 NA NA
L South Korea 2.4 NA .58 NA NA

low-income food-deficit countries (FAO 2011a). The letters before names indicate Global Hunger Indexes (Concern Worldwide 2010); A = alarming, S = serious, M = moderate, L = low. na = data not available. na = no data available. No data available for Cambodia and Taiwan.

SOURCES AND NOTES: FAOSTAT; UNITED NATIONS (2011); IFPRI (2010); HTTP://DATA.WORLDBANK.ORG/TOPIC/POVERTY; FAO (2012B); HTTP://EN.WIKIPEDIA.ORG/WIKI/LIST_OF_COUNTRIES_BY_DISTRIBUTION_OF_WEALTH. THE COEFFICIENT VARIATION (CV) MEASURES THE INEQUALITY OF CALORIC INTAKE ACROSS A GIVEN POPULATION.

Food exporting drives up prices too high for the poor, even of basics. The poor primarily consume cereals because of the higher prices of fruits, vegetables, fish and meat; and their daily calorie consumption has steadily decreased since 1988 (Saxena 2008). In addition to volatile food prices, national social safety nets do not alleviate the inequitable impacts on the poor. According to the Asian Development Bank (2013: 37),

most Asian countries use social safety nets of some kind, intended to shield poor and vulnerable groups from severe deprivation. … On average, poor countries allocate lower proportions of GDP for social protection [than richer countries]. … Moreover, given the inability to accurately target the poor when needed, the effectiveness of existing schemes … is questionable.

In twelve of the Asian fisheries, more than 60 percent of the population earn their livelihoods from agriculture and fishing. Throughout the Asian fisheries, there are sharp inequalities in wealth and income distribution, access to waged jobs, public service delivery, and access to affordable foods, especially between rural and urban households (ADB 2013). According to the World Bank (2013a: 2), “the world’s growing food fish supply gap impacts disproportionately on the nutrition and health of the poor.” Domestically, expanded fish consumption occurs primarily among Asian urban populations, especially the middle classes (Toufique 2015). Rural households cannot afford the foods they produce because of the inequalities in the export commodity chains. Indeed, the rural households that produce food crops and fishery commodities receive much less of the final consumer prices than urban middlemen and export agribusinesses (ADB 2013: 47). As a result, undernutrition, child stunting, anemia, and other nutritional shortfalls occur much more frequently among rural Asian households. Access to food and nutritional shortfalls are also inequitably distributed along gender and age lines, with women and children suffering the highest incidence of hunger and anemia (see Table 2; McLean et. al 2009; Saxena 2008; IFPRI 2016). Ethnic minorities also experience a higher incidence of hunger and nutritional shortfalls than the rest of Asian populations (e.g., Diamond 2011).30 In China, for example, school-age children of western rural provinces are six times more likely to be anemic than their urban peers (Fan et al. 2021), part of this inequality resulting from discrimination against ethnic minorities.

10 Impacts of Wastage on Food Security

Preventing food waste will not insure that the hungry receive any greater share of production, and much of the waste currently occurs after purchase in the richer countries. As Eric Holt-Gimenez (2018: 38) points out, “people go hungry because they are poor, not because food has gone to waste.” However, ending waste in producing territories might increase the amount of fresh food, especially fish, vegetables and fruits, that could be available for local consumption. Cutting food wastage in half would equate to enough food to feed one billion people annually (Rockefeller Foundation 2013). Each year, more than $750 billion worth of food is lost or wasted, endangering both the livelihoods and diets of a high percentage of low-income laborers in developing countries (Grundleger and Stewart 2014). Food losses occur during harvesting and processing while waste ensues during distribution and consumption. When scholars combine losses and waste, they employ the term wastage. A ground-breaking FAO report warns that “roughly one-third of food produced for human consumption is lost or wasted globally, which amounts to about 1.3 billion tonnes per year” (Gustavvson et al. 2011: 3). Consequently, one out of every four calories intended for people is never consumed by them (Lipinski et al. 2013).

In developing countries, food is mainly lost during the early and middle stages of agricultural crop and fishery supply chains. However, waste is minimal because households can only afford smaller amounts that are bought daily, and foods are often eaten even after spoilage begins (Gustavvson et al. 2011). More than three-quarters of these losses occur because of inefficient harvest techniques, inadequate storage and transport infrastructure, defective packaging and the lack of cold chains for preservation of fresh crops and fishery products (ADB 2013: 50–52l; Davy 2013).

Although South and South-east Asia have the second-highest levels of global food loss, accounting for approximately 25% of global food loss, their food waste is minimal. Food loss constitutes 80% of all food wastage– loss plus waste– in the region. The majority of Asia … suffers from infrastructure problems, including poor-quality roads, hot and humid weather (which drives spoilage) and poor packaging, all of which result in large quantities of food lost during production, storage and transit. While the economies of Asian countries are expanding rapidly, this economic expansion has not yet resulted in improved agricultural infrastructure. (Grundleger and Stewart 2014: 9)

Every day in 2009, food and fishery loss and waste eliminated more than 600 calories per capita from the diets of people in our target Asian fisheries (Gustavvson et al. 2011). As Figure 11 shows, 20 percent of cereals, 50 percent of vegetables and fruits, and more than one-third of Asian fishery output is never available for human consumption because it is lost or wasted between harvest and consumption. China, Indonesia, Myanmar and Sri Lanka could have cut their national fishery consumption shortfalls by about two-thirds if losses and waste had been sharply deterred. China generates about 53 million tons of food loss and waste each year, enough to feed more than half the undernourished people residing there (Marchisio 2020). Similarly, the national fishery shortfalls of Bangladesh, Pakistan, the Philippines, South Korea, Thailand, and Viet Nam could have been slashed by about half if loss and waste had been averted. Even those countries with the highest fishery shortfalls– India, Japan, Malaysia, North Korea– could have lowered those nutritional deficiencies by one-third through prevention of losses and waste.31

FIGURE 11
FIGURE 11

Percentage of food wastage, in East, South and Southeast Asia, 2010

SOURCE: ANALYSIS OF GUSTAVSSON ET AL. (2011). FOODS ARE GROUPED ACCORDING TO FAOSTAT FOOD BALANCE SHEETS. PULSES AND SEEDS INCLUDE SOY AND NUTS

However, current estimates of wastage exclude a growing problem in global food security. Increasingly, foods are never consumed by humans because they are either contaminated or diseased. In rich countries, foods are frequently recalled or destroyed because they were contaminated with threats to humans in the production or distribution processes (e.g., E-Coli in lettuce in the US in 2018 and 2019). In addition, large numbers of livestock are destroyed almost every year because they are infected with diseases (e.g., the Mad Cow scare in Europe). Between August 2018 and June 2019, several East and Southeast Asian countries experienced the largest animal disease outbreak in history. African swine flu spread throughout the pork industry, eliminating 3.7 million hogs. The FAO predicted in June 2019 that China, which accounts for half of the world’s pork production, would lose one-third to one-half of its swine before the epidemic’s end. Because East and Southeast Asia produce about three-fifths of the world’s pork, 2019 pork prices rose globally and throughout Asia (Dinh and McNeill 2019; FAO 2019b).32

11 Looking to Future Chapters

In Chapters 2 through 6, we will shift our lens from regional to national and local community levels. By focusing on one of the Asian fisheries, we will explore, in more human terms, the threats to Asian food security that have been identified in this chapter. We will offer an in-depth case study of the Philippines, a country that has declined from food sufficiency to dependence on imported foods and fish– even though it has maximized exploitation of its natural resources.

1

Analysis of crop and fishery outputs in FAO (2017a, 2018). Throughout this chapter, monetary values are expressed in $US.

2

Export statistics are derived from analysis of FAOSTAT, FAO (2012b) and FAO (2012e).

3

In 2015, North Korea lost half its food crop production to the worst drought in a century (Sang-Hun 2015).

4

Anemia is mild (15 percent or less) only in Japan.

5

WHO Global Database on Vitamin A Deficiency.

6

WHO Global Database on Iodine Deficiency.

7

Analysis of FAO (2018).

8

The food deficient high capture fisheries were Bangladesh, India, Indonesia, North Korea, Pakistan, the Philippines, and Sri Lanka. The food deficient high aquaculture producers were Bangladesh, India, Indonesia, Pakistan, and the Philippines. Note that Bangladesh, India, Indonesia, Pakistan, and the Philippines were food-deficient even though they were high producers/exporters in both fishery categories.

9

Analysis of ADB (2012: 134, 235), with dollars standardized to 2010 value.

10

See, for example, the overestimation of China’s human consumption levels because Chen and Duncan (2008: 188) ignored both nonfoods and wastage.

11

This was the National Forum for Catamaran and Country Boat Fishermen’s Rights.

12

WHO Global Database on Iodine Deficiency; WHO Global Database on Vitamin A Deficiency.

13

We thank Professor Clelland (1935–2021) for providing this unpublished theoretical explanation not long before he died. For his published work on dark value drains, see Clelland (2013, 2014, 2015a, 2015b).

14

Asche et al. (2015) analyze a “seafood trade deficit” in which developing countries engage in the pattern of exporting higher valued seafood and importing lower valued seafood. However, they do not draw any direct connections to nutritional inequality.

15

Analysis of FAOSTAT data.

16

From Asian fisheries, the primary crustacean exports are prawns, shrimp, crab and lobsters while the mollusks primarily include oysters, clams, conches, blue mussels, cuttlefish, octopus, squid., and more rarely from the Sea of Japan, abalone, and scallops.

17

Aggregation and analysis of UN COMTRADE statistics.

18

Analysis of Japanese food exports and trading partners, UN COMTRADE database.

19

Analysis of food crop outputs, FAO (2017a).

20

Aggregation and analysis of data in FAO (2010).

21

Aggregation and analysis of imports, UN COMTRADE database.

22

Historically, these fisheries imported a great deal of their wheat from the USA, but this pattern has shifted over the last decade. By 2013, these fisheries were purchasing wheat primarily from Canada, Ukraine, Russia and Australia (Analysis of Asian wheat imports, UN COMTRADE database.)

23

Five of the world’s top ten soya producers are situated in South America: Brazil (2nd), Argentina (3rd), Paraguay (6th), Uruguay (8th) and Bolivia (10th).

24

Aggregation and analysis of import data, UN COMTRADE database.

25

Aggregation and analysis of import data, UN COMTRADE database.

26

For impacts on China’s rural communities, see Song and Chen (2006).

27

Aggregation and analysis of country data in FAO (2010, 2011b).

28

Coconuts could be used domestically to meet protein shortfalls.

29

Only Taiwan and South Korea were ranked with low risk. North Korea was not listed.

30

Scholars, international organizations and Asian national government programs have published very little about hunger and nutritional inequalities experienced by Asian minority groups.

31

Part of fishery losses indirectly re-enter human food chains through conversions of fish meal, silage and sauce that is used in aquaculture and livestock feeds (Ghaly 2013).

32

The European Union is the world’s top exporter of pork. African swine flu outbreaks occurred in Eastern and Northern Europe between 2007 and 2018 while the first outbreak in Asia occurred in China in August 2018 (Marks 2018).

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