Dr. Mae-Wan Ho finds
strong allies for her idea on sustainable systems as closed cycles modelled
on the organism (Dream
Farm 2 - Story So Far) during her recent visit to China , especially
in a land-water farming system developed over the past two thousand years
Getting the most from land and water
The clouds and mists cleared as we prepared to land in Guangzhou,
and a remarkable landscape came into view. Like a mosaic of silver mirrors
embedded in emerald, hundreds, if not thousands of ponds filled the spaces
between the Pearl River tributaries as they meandered and fanned out into
the South China Sea.
The ponds were predominantly
narrow rectangles stacked broadside on, with shorter rectangles, squares,
and irregular shapes pressed into service to fit the topography. The main
effect was to leave cultivated strips of land and the occasional fields between
adjacent bodies of water.
The Pearl River Delta of
South China, sprawling over 12 000 km2,
is famous for its dyke-pond system of fish farming combined with the cultivation
of crops . It contains one of China’s richest and most densely populated
agricultural areas, supporting an average of 17 persons per hectare.
The dyke-pond system evolved
over the past two thousand years, perfected by generations of Chinese farmers
into a ‘circular’ economy of intensive agriculture integrated with the polyculture
of carps and other freshwater fishes, on a geographic and economic scale unrivalled
elsewhere in the world. It depends on maximising internal inputs between land
and water, optimising the efficient use of resources while minimising wastes.
The director of the Guangzhou
Institute of Geography, Prof. Zhang Hongou, stressed that ‘circular economy’
is a guiding principle in mainstream Chinese thinking, as opposed to the linear
economy of the West. Perhaps that is at least partly why the Chinese economy
has been growing mostly in double figures over the past decade.
Guangzhou Institute of Geography
was established in 1958 as part of the Chinese Academy of Sciences,
and in 1999, received recognition from the Chinese government as one of Ten
National Distinguished Organisations. Among its accolades is the scientific
study of the dyke-pond system pioneered by Prof. Zhong Gongfu and his colleagues
in the 1970s, and its successful extension for flood control and improved
land use (see later).
The Institute also researches on regional development in Guangdong,
tropical and Chinese geography, environment and ecology, remote sensing and
land use. It runs a web resource for remote sensing and environmental protection,
and publishes a journal.
The dyke-pond system
In the late 1980s when Guangzhou Institute first carried out the survey,
the main dyke-pond area covered 86 632 ha between the two major Pearl River
tributaries, Xijiang and Beijiang, of which 30 321 ha (35 percent) were fishponds,
combined with the cultivation of mulberry (10 395 ha, 12 percent) or sugar
cane (15 593 ha, 18 percent). The remainder 30 322 ha (35 percent) was mainly
irrigated rice (25 percent) and a variety of mixed or miscellaneous agriculture
that includes dykes specialising in fruit trees, vegetables or decorative
plants and flowers .
The pond is the heart of the system. To produce a pond, soil is excavated
and used to build or repair the dykes surrounding it. Before it is filled
with water, the pond is prepared by clearing, cleaning and fertilization with
quick lime, tea-seed cake and organic manure from livestock kept on the dykes.
Most ponds are rectangular, 0.4 to 0.6 ha in area and 2 to 3 m deep. The dykes
are usually 6 to 10 m wide, and extend 0.5 to 1.0 m above the pond surface.
Various fish species live at different pond depths, and have different feeding
habits, thereby making full use of the water and the pond ecology. The typical
polyculture is a combination is the “four big family fish”: grass carp (Ctenopharygodon
idellus), silver carp (Hypopthalmicths molitrix), big head carp
(Aristichthys nobilis) and common carp (Cyprinus carpio), requiring
little or no external input.
The pond mud, much enriched in nutrients, serves as fertiliser for crops.
Ponds are drained two or three times a year, and the mud at the bottom is
dredged up to put on the dykes, thereby raising and repairing the dykes and
restoring the depth of the pond. Pond mud is also used for mushroom cultivation.
Mushrooms are often cultivated on the floor of the silkworm shed in winter,
the off-season for silkworm production. After the final crop of mushrooms
has been harvested, the mud-bed is used to fertilize vegetables, fruit trees
The pond is filled with river water. Water also enters directly as rain and
through runoffs from the dykes. Water leaves the pond via the pond drainage
outlet in controlled discharges. It is also lost through evaporation and transpiration,
via seepage into the dykes, and through being removed at regular intervals
to ‘fertigate’ the crops growing on the dykes.
Livestock is an important link in the circular economy. Pigs, chickens and
ducks are reared on the dykes, to provide manure to fertilise the fishponds,
to encourage the growth of plankton that feed the fish.
Most dyke crops are fed directly to the fish, such as elephant grass for
the grass carp, or else to the livestock, such as forage crops for pigs.
With a tropical to subtropical climate, the dyke-pond area is well endowed
with sunshine and rainfall, and hence extremely productive, especially with
a system that recycles and transforms all the “wastes” into nutrient resources.
The circular economy can be quite complex [1-3]. I have drawn a diagram of
a simple system involving mulberry cultivation. Mulberry leaves are picked
to rear silkworms, from which silk cocoons are harvested, while the wastes
of silkworms are used to fertilise the pond to feed the fish. With only pigs
and vegetables included, there are at least 11 cycles in the diagram varying
in length from two to five links.
The external energy input is minimal, and consists of mainly labour and the
energy expanded to make farming implements, housing and equipment for rearing
silkworms, and machinery and energy to aerate the fishpond and to dredge it.
The major energy input by far, of more than 99 percent , is sunlight, and
it is free.
There are numerous harvests, fishes, silk cocoons and vegetables being the
major ones for the system depicted, pigs would be a minor harvest. Some harvests
would include livestock such as chickens and ducks as well as mushrooms.
Fish sales contribute the largest source of income to the region’s agricultural
sector, some 50 percent of the total fish production of Guandong Province
and 80 percent of the nation’s export in live fish.
Figure 1. Circular economy of dyke-pond system
Since the late 1970s, the traditional dyke-pond system of the Pearl River
Delta has been undergoing dramatic changes. The first was a major shift from
a collectivist to household production as part of the major rural reforms
implemented throughout China. The second involves an intensification of production,
a gradual supplementation of internal inputs with external inputs and a move
away from the previously sustainable circular economy.
Dyke-pond system and flood control
About 1 000 years ago, the coastline of the Pearl River Delta was very different.
The delta of Zhujiang, the most northern of the three major tributaries, met
the delta of Xijiang, the most southern tributary , and the lowlands were
neither widely nor continuously cultivated on account of flooding and the
presence of sulphuric acid soils. The villagers depended heavily on capturing
and collecting marine, riverine and wetland resources. At higher elevations,
however, fruits were cultivated, especially litchi (Litchi chinensis)
and longan (Euphoria longana).
During the mid-fourteenth century, water control measures were started in
the lower-lying areas. Small watercourses were dammed and dykes created to
make fishponds. Ponds were dug to drain the marshes and natural ponds in order
to create agricultural land, and the excavated soil was used to construct
the dykes. The fishponds were stocked with carp fry naturally occurring in
The first commercial crops to be grown on the dykes were litchi and longan,
but there were no conscious effort to integrate pond and dyke ecology until
much later. By the 1620s, mulberry was widely cultivated on the dykes and
the economic returns from the integrated mulberry dyke-fish pond systems were
found to be greater than fruit-tree cultivation.
Thus, the circular economy of the dyke-pond system evolved out of a flood
control measure, and it has been used effectively for the same purpose since.
It will have worldwide applications as sea level rises in coastal areas, and
in flood-prone areas fed by melting ice and glaciers.
Outside the core region of the traditional dyke-pond system, there remains
in Guangdong Province some 200 000 ha of flood-prone lowland, including the
areas along the lower reaches of the main rivers and the coastal lowlands
of the Zhujiang Delta. Most of these lowlands are seasonally flooded to depths
of 1 to 1.5 m, and sometimes as much as 3 m of river and rainwater, exacerbated
by a history of deforestation in the watersheds of Guangdong Province.
Since the 1950s, various measures have been taken to manage the flood-prone
lands: building reservoirs and canals, contour ditching, sluice systems to
raise the water in canals and to drain floodwaters; establishing a network
of pumping stations to drain water from the flood plains into the canals;
and reforestation in the highlands. In the coastal regions, earthern dykes
were reinforced or replaced by concrete to improve resistance to typhoon-driven
high hides, irrigation and drainage systems were separated by tunnels to lower
the water-table, an electric pumping network was installed for drainage and
irrigation and low-lying land was elevated by spreading soil.
These measures succeeded in reclaiming much of the flood-prone lowland, making
agriculture possible and improving public health. Schistosomiasis (a disease
spread by a parasitic worm) was eradicated. However, some 30 percent of the
lowland by the rivers in Guangdong still remained to be brought into sustained
productive use. This consists of widely scattered land in small pockets, or
especially low-lying and not amenable to reclamation by other measures. Similarly,
in the coastal zone, despite the use of pumping stations for drainage and
irrigation, crops yields remained low owing to high water tables and salination.
The dyke-pond system has proven effective in transforming those waterlogged
lowlands into productive sites. Fishponds were dug and the excavated sediment
used to construct raised dykes and fields.
Scientists in the Guangzhou Institute of Geography started a research project
in the early 1970s supported by the United Nations University [1-3, 5]. They
established an experimental station in Shunde County in the heart of the dyke-pond
region to study energy flow and material cycles in the newly established dyke-pond
systems, and were able to document the successes .
Turning water-logged lowlands into productive dyke-pond systems
Deqing County, 240 km west of Guangzhou is one of the most seriously eroded
regions in the Province. Many watercourses got silted up and the streambeds
became higher than the surrounding fields, with the result that about 10 percent
of the fields were waterlogged. Two tracts of lowlands were selected for introducing
the dyke-pond systems in 1979.
The first, a 19 ha tract called Liangqintang normally yielded a single rice
crop yearly, and was used for fish culture during the high-water season. Productivity
was low, no more than 3.75 tonnes of rice/ha and 0.75 tonnes of fish/ha. Often,
production failed altogether; and people referred to it as “a tract of three
harvests in ten years”.
The tract was converted to a dyke-pond system growing bananas and elephant
grass (for fish feed). A small distillery and pigsties were constructed next
to the pond. The distiller’s grain was fed to the pigs and the pig wastes
emptied into the pond. The 1981 fish harvest reached 3.0 tonnes/ha. In 1982,
the total harvests (over all 19 ha) jumped dramatically to 125 tonnes of fish,
150 tonnes of bananas, and 75 tonnes of pork, not counting large amounts of
vegetables. The net income for 1981 was already 7.6 times higher than in 1978
before the project began.
The second site selected in Deqing County was a tract of 2.7 ha of seasonally
flooded lowland along the Xijiang River in Quianhoujie Village. It was converted
into a mulberry dyke-pond with some vegetables. A pigsty was constructed near
the pond. Mulberry leaves were fed to silkworms, the silkworm excrement and
pig manure were emptied into the pond. The pond mud was used periodically
to fertilize the dyke soil. By 1982, the net income increased 200 percent
from 1981; and that in 1983 was 60 percent higher than 1982.
Doumen County, located in the southwestern part of the Zhujian Delta, has
40 percent of its land at 0.2 to 0.8 m below sea level. Electric pumps are
commonly used to remove water from low-producing rice and sugarcane fields.
A variety of dyke-ponds were successfully installed in the late 1970s, which
then spread to the whole country.
The low-lying fields at Anfenwei in east Doumen are inundated annually for
several months. Since 1979, 6 ha of fish ponds were dug to a depth of 2.5
to 3 m and the mud removed was spread over the fields at an average rate of
750 m3/ha/year. After several years, the fields were raised to
sea level and no longer water-logged. The fields were planted in a rice-sugarcane
rotation and interplanted with vegetables. Pigs and poultry were raised close
to the ponds and their excrement emptied into the ponds. Rice yields increased
from 6 tonnes/ha/year to 7.5 tonnes/ha/year, and 4 tonnes of fish were harvested
in addition to pigs and poultry. Electricity bills were reduced 20 to 30 percent
annually because of decreased need for drainage pumping. Up to 1982, at least
700 ha of fish ponds have been dug in the entire county, and about 10 000
ha of low-lying fields have been elevated.
The Chenhai-Raoping district of 48.6 km2 situated between Changhai
and Raoping Counties in east Guangdong Province resulted from a reclamation
and farming project completed in 1971. However, much of the area is still
A research team from the Guangzhou Institute of Geography designed an integrated
development programme including the dyke-pond system , and put the programme
into operation in 1983. By 1987, remarkable improvements were achieved in
all aspects, including the dyke-pond system. A total of 262 ha of ponds had
been constructed yielding 5.805 tonnes fish/ha at a value of 6.08 million
Yuan/year. Considerable amounts of vegetables and forage crops were also harvested
from the dykes.
Dyke-pond system under pressure from industrial growth
These remarkable successes were not followed up, however. Practically all
the academics involved in the dyke-pond projects had soon retired or were
near retirement, and market forces and other pressures of rapid industrialisation
came into play.
“China has developed too quickly, at 10 to 20 percent growth in GDP a year,”
the Institute director Prof. Zhang said, “This has placed agriculture under
great pressure. Industrialisation has led to a decrease in land available
for agriculture, and the pressure to produce more from less land has resulted
in increased pollution.”
The professors of the dyke-pond system, Zhong Gonfu, Wu Houshui, Deng Hanzeng
and Liang Kuo Ziao, now all retired, came to meet with us to explain their
work, thanks to the tireless efforts of Prof. Zhong Ying, daughter of Zhong
Gongfu, who acted as our guide and mentor throughout the most enjoyable and
productive five days we had in Guangzhou. She and Prof. Wu Houshui accompanied
us for a day tour to important sites, including the dyke-pond region, or what
is left of it today.
The experimental station where they carried out precise measurements on energy
and material flows has long since gone, and many of the sites they surveyed
or worked on have disappeared. Prof. Wu Houshui estimates that perhaps half
of the pond-dyke area may have gone under the pressure of industrial development.
All agreed that there was a need for projects like Dream Farm 2  (Dream
Farm 2 - Story So Far) to integrate biogas production and other renewable
energies with sustainable agricultural production. Prof. Zhang Hongou was
very receptive to the idea, and we agreed to develop future collaborations.
Industry, ingenuity and market forces
The success of the dyke-pond system owes a lot to the particular combination
of ingenuity and industry of Chinese farmers, and it is still much in evidence
The farmers are extremely skilled at maximising the use of space, time and
resources; but a commitment to hard work is also necessary. Gourds and melons
are trained on trellises overhanging ponds and drainage ditches, and crops
are planted together so that sun-loving species provide shade for those requiring
it. Plantings are timed so that several harvests are obtained from the same
piece of land.
Where sugarcane is planted, the main product is sugar, but the young leaves
are fed to fish and pigs, and old leaves used to shade vegetable gardens.
Refinery wastes are returned to the dyke pond as fish and animal feed. Bamboos
are often planted to provide poles for construction and materials for making
baskets, traps, screens, trellises and frames. Bamboo wastes are also used
During our all too brief tour of the dyke-pond region, we met a farmer by
the roadside, knee deep in the drainage ditch, dredging up the black mud from
the bottom of the ditch to put onto her vegetable garden that reached right
up to the water margin of the ditch. Her garden is a perfect example of the
intensive and ingenious use of limited land. The Chinese government gave her
one fen of land (one-tenth of a Chinese mu = 0.0667 ha), but she grows enough
to feed her own family, with plenty left over to sell on the market. She offered
to invite us to lunch on the spot, on hearing that we were from London in
the UK; unfortunately we were unable to accept her due to the lack of time.
Other ingenious use of the pond was to raise ducks, the faeces of which go
directly to fertilise the fish and we saw plenty of that.
Fish farming can be very profitable, but is also increasingly at the mercy
of market prices. Chinese love good food to extreme, and restaurant meals
are a must for any visitors (fortunately for us). The foyer of restaurants
in Guangzhou is typically filled with aquariums exhibiting live fish that
you can choose for your meal with the price per catty clearly marked, and
it is considered impolite to choose cheap fish for the guests. Any fish that
became too available would become cheap, no matter how tasty it is, and hence
could bankrupt the fish farmer overnight.
We saw signs of intensification of fish farming that was clearly unsustainable.
A worker was hired to feed cut-up frozen sea fish to some highly priced carnivorous
fish reared in a pond owned by someone else, and the feeding shed was filled
with “fish medicines” to control diseases and parasites probably brought in
by the feed, and by the pond being too heavily stocked. The price of the feed
was 1.50 Yuan per catty, while the fish in the pond was fetching $15 per catty
in the market.
High stocking rates of fishponds, external feeds, diseases, and “fish medicines”
all contribute to fouling the pond water, which becomes a serious source of
pollution when drained into the rivers and lakes. Intensive fish farming has
indeed become an ecological problem in search of a solution, and Dream Farm
2  could well offer a way forward.
Ruddle R and Zhong F. Integrated agriculture-aquaculture
in South China. The dike-pond system of Zhujiang Delta, Cambridge University
Press, Cambridge, 1988.
Zhong G, Wang Z and Wu H. Lan-water Interactions
of the Dike-Pond System, Presses Universitaires de Namur, Namur, 1997.
Deng H. The dyke-pond agro-ecosystem of the Zhujiang
(Pearl River) Delta, China. Arch Hydrobiol
Beih Ergeb Limnol 1987, 28, 421-3.
Li CX. Village Annals of Jiujiang, Nanhai, 1657
Deng H. Application of dike-pond systems to degraded
lands of South China. In Parham WE et al (eds), Improving Degraded Lands: Promising Experiences
from South China, Bishop Museum, Honolulu, 1993 (in Chinese).
Fan XP. On the development and management of Chenghai-Raoping
Reclamation Area. Tropical Geography 1985, 5, 34-43.