The cultivation of transgenic pest-resistant cropsmay reduce pesticide application, improve production and increase economic benefit. Breeding and planting transgenic pest-resistant crops is expected to be a promising way to control pests. Pest-resistant transgenic researches in China began in the early 1990s. In 1992, China developed the country’s first Bt protein gene (CryIA gene) with the intellectual property right of its own. Up till now, the exogenous genes, such as Bt protein gene, trypsin inhibitor gene (CpTI gene), etc., have been transformed into cotton, and more than 50 commercially approved transgenic cotton varieties were developed. Since the 1970s, with the widely uses of chemical pesticides in cotton production, the pesticide-resistance of cotton bollworm (Helicoverpa armigera (Hubner)) dramatically enhanced. Cotton acreage in China declined from 6.835 million ha in 1992 to 4.985 million ha in 1993. In subsequent years, cotton bollworm seriously occurred every year. Since 1998 the adoption of insect-resistant varieties has effectively controlled the outbreak of cotton bollworm. Since the late 1990s, the cultivation area of transgenic insect-resistant cotton in China has been rapidly expanding, and its proportion in the total domestic cotton planting area has been increasing year by year. In 1998, transgenic insect-resistant cotton began to be planted in the Yellow River valley, and that year’s acreage reached 240,000ha, only 5.4% of the total cotton planting area; The planting area increased to 647,000ha, 1.2 million ha, 1.933 million ha, 1.867 million ha, 3.067 million ha, and 3.104 million ha in the years 1999–2004, accounting for 17%, 31%, 40%, 45%, 60%, and 50% of the total area, respectively. The planting area of domestic transgenic insect-resistant cotton accounted for 30%, 60%, and 70% in the years 2002–2004. Due to the cultivation of transgenic insect-resistant cotton, pesticide application in China reduced by 123,000 t and cotton yield increased by 9.6% during the three years 1999–2001. Currently, almost all of the planted cotton in Hebei, Henan, and Shandong Province is transgenic insect-resistant cotton. In the Yangtze River valley, transgenic insect-resistant hybrid cotton holds the dominant position and its planting W.J. Zhang (B) Research Institute of Entomology, School of Life Sciences, Sun Yat-sen University, Guangzhou 510275, China e-mail: zhwj@mail.sysu.edu.cn R. Peshin, A.K. Dhawan (eds.), Integrated Pest Management: Dissemination and Impact, DOI 10.1007/978-1-4020-8990-9 18, ©C Springer Science+Business Media B.V. 2009 525 526 W.J. Zhang and Y. Pang area has been growing in the past years. So far, the total planting area of transgenic insect-resistant cotton in China has reached 4.667 million ha, with an average income of 2,130∼2,400 RMBYuan/ha. Annual reduction in chemical pesticide application reaches 20,000∼31,000 t, equivalent to 7.5% of China’s annual total production of chemical insecticides. Breeding of transgenic insect-resistant rice in China developed quickly in the past years. To date, CryI, CpTI, and GNA genes, etc., have been transformed into the rice, and some insect-resistant rice varieties (strains) were developed in China. They can be used to suppress rice insect pests such as Chilo suppressalis (Walker), leafrollers, and brown planthopper. Researches showed that the adoption of transgenic insect-resistant rice can reduce 70∼80% of insecticide application and would not affect the rice biodiversity. From recent years’ field trials in Hubei and Fujian, indicated that insecticides were seldom used throughout the growing season and rice yield can increase by 12%. So far, the safety evaluations and experiments on the commercial production of transgenic insect-resistant rice have not yet showed any significant security issues. However, as rice is the main food crop in China, the application for commercialization of transgenic rice has never been approved. In addition to cotton and rice, the insect-resistant transgenics for wheat, soybean, maize, and other crops have being made in China. China has imported some of the transgenic crops and resulted in certain impacts. For example, due to the low production cost and better quality, the transgenic soybean of the United States exhibits the obvious economic advantages. The import of transgenic soybean of the United States resulted in the serious stock of domestic soybean production, and undermined the economic interests of Chinese farmers. So far, the most significant negative impacts for planting transgenic insectresistant crops, in particular cotton, are the outbreak of secondary pests and the impairment of arthropod community, etc. Due to the problems of planting transgenic insect-resistant crops, such as the narrow insect-resistance spectrum, the increased resistance of insect pests to transgenic crops, the possible outbreak of secondary insect pests, and the potential environment and biodiversity risks, it is necessary to follow IPM principles and combine the other control measures. Chinese scientists have summarized the practical problems in planting transgenic insect-resistant crops and explored various IPM measures, such as resistance management, intercropping, seed purifying, protection of natural enemies, etc., to address these problems. The IPM measures have being implemented in China.
[1]
W. Zhai,et al.
Introduction of a rice blight resistance gene,Xa21, into five Chinese rice varieties through anAgrobacterium-mediated system
,
2000,
Science in China Series C: Life Sciences.
[2]
Wenjun Zhang.
Computer Inference Of Network Of Ecological Interactions From Sampling Data
,
2007,
Environmental monitoring and assessment.
[3]
J. Losey,et al.
Transgenic pollen harms monarch larvae
,
1999,
Nature.
[4]
Wenjun Zhang.
Pattern Classification and Recognition of Invertebrate Functional Groups Using Self-Organizing Neural Networks
,
2007,
Environmental monitoring and assessment.
[5]
Kong Luen Heong,et al.
The role of biodiversity in the dynamics and management of insect pests of tropical irrigated rice—a review
,
1994
.
[6]
D. Andow.
Vegetational Diversity and Arthropod Population Response
,
1991
.
[7]
A. Saegusa.
Japan tightens rules on GM crops to protect the environment
,
1999,
Nature.
[8]
WenJun Zhang,et al.
Supervised neural network recognition of habitat zones of rice invertebrates
,
2007
.
[9]
Sun Xiao-fen.
GNA Confers Resistance to Rice Brown Planthopper in Transgenic Rice Pure Lines by Both Bioassay and Feeding Tests
,
2001
.
[10]
Q. Fu,et al.
Effects of insect-resistant transgenic rice lines MSA and MSB on non-target pests Nilaparvata lugens and Sogatella fucifera
,
2003
.
[11]
Liu Yu.
Evaluation of the effects of insect-resistant cry1Ac/sck transgenic rice on the parasitoid communities in paddy fields
,
2006
.
[12]
Z. Hong,et al.
Effect of transgenic Cry1 Ac+CpTI cotton (SGK321) on population dynamics of pests and their natural enemies
,
2004
.
[13]
Donglin Huang,et al.
Effects of Zhongmiansuo 45 and Zhongmiansuo 41 on experimental population of {\sl Spodoptera litura}
,
2006
.
[14]
Jikun Huang,et al.
'Bt cotton' benefits, costs and impacts in China
,
2003
.
[15]
Wang Hong-liang.
Advance in research on integrated pest management
,
2006
.
[16]
A. Hilbeck,et al.
Effects of transgenic Bacillus thuringiensis corn-fed prey on mortality and development time of immature Chrysoperla cornea (Neuroptera: Chrysopidae)
,
1998
.
[17]
Mcpo Box.
Effects of Bt transgenic rice on population dynamics of main non-target insect pests and dominant spider species in rice paddies
,
2002
.
[18]
M. Rice,et al.
Preimaginal Development, Survival, and Field Abundance of Insect Predators on Transgenic Bacillus thuringiensis Corn
,
1997
.
[19]
Fred Gould,et al.
Potential and problems with high‐dose strategies for pesticidal engineered crops
,
1994
.
[20]
S. G. Rogers,et al.
Insect Tolerant Transgenic Tomato Plants
,
1987,
Bio/Technology.
[21]
H. Cui,et al.
Evaluation of the impact of insect-resistant transgenic rice on the feeding and oviposition behavior of its non-target insect, the brown planthopper, Nilaparvata lugens (Homptera: Delphacidae)
,
2004
.
[22]
N. Seetharama,et al.
Prospects for using transgenic resistance to insects in crop improvement
,
2000
.
[23]
P. Yufa,et al.
Research Advances in Ecological Safety of Insect-Resistant Transgenic Rice
,
2006
.
[24]
G. Head,et al.
Evaluation of dietary effects of transgenic corn pollen expressing Cry3Bb1 protein on a non‐target ladybird beetle, Coleomegilla maculata
,
2002
.
[25]
Wenjun Zhang,et al.
Impact of IPM and Transgenics in the Chinese Agriculture
,
2009
.
[26]
M. Montagu,et al.
Transgenic plants protected from insect attack
,
1987,
Nature.
[27]
James Kling.
Could Transgenic Supercrops One Day Breed Superweeds?
,
1996
.
[28]
H. R. Whiteley,et al.
Bacillus thuringiensis §-Endotoxin Expressed in Transgenic Nicotiana tabacum Provides Resistance to Lepidopteran Insects
,
1987
.
[29]
Wenjun Zhang,et al.
Function Approximation and Documentation of Sampling Data Using Artificial Neural Networks
,
2006,
Environmental Monitoring & Assessment.
[30]
S. Datta,et al.
Effects of Bt transgenic rice on population dynamics of main non-target insect pests and dominant spider species in rice paddies.
,
2002
.
[31]
Chenlan Mao.
Impact Evaluation of Insect-Resistant Transgenic Rice on the Feeding and Oviposition Behavior of Its Non-Target Insect, the Brown Planthopper, Nilaparvata lugens (Homptera: Delphacidae)
,
2003
.
[32]
D. Pimentel,et al.
CONSERVING BIOLOGICAL DIVERSITY IN AGRICULTURAL/FORESTRY SYSTEMS
,
1992
.
[33]
E. Oerke.
Crop Production and Crop Protection: Estimated Losses in Major Food and Cash Crops
,
1994,
The Journal of Agricultural Science.
[34]
W. Fei,et al.
Effects of Transgenic Bt Cotton on Main Pests and Community of Natural Enemies in Cotton Fields
,
2004
.