Main environmental factors for forestry insects that become important pests

WANG Yi-ping; YU Zhen-dong; WU Hong

Dec. 2007

Article Contents

Article Navigation > Journal of Zhejiang A&F University > 2007 > 24(6): 752-757

WANG Yi-ping, YU Zhen-dong, WU Hong. Main environmental factors for forestry insects that become important pests[J]. Journal of Zhejiang A&F University, 2007, 24(6): 752-757.

Citation:

WANG Yi-ping, YU Zhen-dong, WU Hong. Main environmental factors for forestry insects that become important pests[J]. Journal of Zhejiang A&F University, 2007, 24(6): 752-757.

Main environmental factors for forestry insects that become important pests

1. School of Forestry and Biotechnology, Zhejiang Forestry College, Lin'an 311300, Zhejiang, China;
2. Yuhang Ministry of Forest and Water Conservancy, Hangzhou 311100, Zhejiang, China

Received Date: 2006-11-14
Rev Recd Date: 2007-04-13

Abstract

This paper discussed why some insects become pests with primary reasons being clarified in order to control pest of forest in the future. These reasons included drought, atmospheric pollution, consequences of global change, and exotic invasive species. Moreover, three key points for rationally allocating different tree species to forests, so as to prevent pest disasters, were put forward, namely:biodiversity to enhance ecosystem stability, a risk dispersing mechanism, and a relative resistance principle. Based on regulation of tree species distribution and time-space structure in forest ecological systems must either promote pest control or at least not increase forest pest damage.
- forest protection,
- forest pest,
- review,
- atmospheric pollution,
- drought,
- consequences of global change,
- exotic invasive species

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References

[1]	HUGHES P R, CHIMENT J J, DICKIE A I, et al. Effect of pollutant dose on the response of Mexican bean beetle to SO₂-induced changes in soybean[J]. Env Ent, 1985, 14(6):718-721.
[2]	RIEMER J, WHITTAKER J B. Air pollution and insect herbivores:observed interactions and possible mechanisms[M]//Insect-Plant Interactions.Boca Raton:CRC,1989:73-105.


[5]	ZVEREVA E L, KOZLOV M V. Effects of air pollution on natural enemies of the leaf beetle Melasoma lapponica[J]. J Appl Ecol, 2000, 37(2):298-308.
[6]	ZVEREVA E L, RANK N E. Host plant effects on parasitoid attack on the leaf beetle Chrysomela lapponica[J]. Oecologia, 2003, 135:258-267.
[7]	ZVEREVA E L, KOZLOV M V, HAUKIOJA E. Population dynamics of a herbivore in an industrially modified landscape:case study with Melasoma lapponica(Coleoptera:Chrysomelidae)[J]. Acta Phytopathol Entomol Hung, 1997, 32:251-258.
[8]	ZVEREVA E L, KOZLOV M V, NEUVONEN S. Decrease of feeding niche breadth of Melasoma lapponica(Coleoptera:Chrysomelidae) with increase of pollution[J]. Oecologia,1995,104:323-329.
[9]	ZVEREVA E L, KOZLOV M V, NEUVONEN S. Population density and performance of Melasoma lapponica(Coleoptera:Chrysomelidae) in surroundings of a smelter complex[J]. Environ Entomol, 1995, 24:707-715.
[10]	ZVEREVA E L, KOZLOV M V, NIEMELA P. Effects of leaf pubescence in Salix borealis on host-plant choice and feeding behaviour of the leaf beetle Melasoma lapponica[J]. Ent Exper Appl, 1998, 89:297-303.
[11]	ZVEREVA E L, KOZLOV M V, NIEMELA P, et al. Delayed induced resistance and increase in leaf fluctuating asymmetry as responses of Salix borealis to insect herbivory[J]. Oecologia, 1997, 109:368-373.
[12]	PIMENTEL D. Insect population response to environmental stress and pollutants[J]. Env Review, 1994, 2(1):1-5.
[13]	KOZLOV M V, NIEMELA P. Difference in needle length-a new and objective indicator of pollution impact on Scots pine (Pinus sylvestris)[J]. Water Air Soil Poll, 1999, 116:365-370.
[14]	KOZLOV M V, ZVEREVA E L, NIEMELA P. Shoot fluctuating asymmetry-a new and objective stress index in the Norway spruce (Picea abies)[J]. Can J For Res, 2001, 31:1289-1291.
[15]	KOZLOV M V, WILSEY B J, KORICHEVA J. Fluctuating asymmetry of birch leaves increases under pollution impact[J]. J Appl Ecol, 1996, 33:1489-1495.
[16]	PORT G R, THOMPSON J R. Outbreaks of insect herbivores on plants along motorways in the United Kingdom[J]. J Appl Eco, 1980, 17:649-656.
[17]	NEILSON R P, MARKS D. A global perspective of regional vegetation and hydrologic sensitivities from climatic change[J]. Veget Sci, 1994, 5:715-730.
[18]	SAIKKONEN K. Nuclear polyhedrosis virus of the European pine sawfly (Neodiprion sertifer) retains infectivity in soil treated with simulated acid rain[J]. J Appl Ent, 1995, 119(3):495-500.
[19]	NIELSEN J K, HANSEN M L, AGERBIRK N, et al. Responses of the flea beetles Phyllotreta nemorum and P. cruciferae to metabolically engineered Arabidopsis thaliana with an altered glucosinolate profile[J]. Chemoecology, 2001, 11:75-83.
[20]	MCINTOSH R L, ALLISON J D, et al. Comparative effcacy of five type of trap for woodborers in the Cerambycidae, Buprestidae and Siricidae[J]. Agric For Entomol, 2001, 3(2):113-120.
[21]	EAMUS D, JARVIS P G. The direct effects of increase in the global atmospheric CO₂ concentration on natural and commercial temperate trees and forests[J]. Adv Ecol Res, 1989, 19:1-55.







[29]	-164.
[30]	SOLTER L F, KEENA M. Infectivity of four species of nematodes (Rhabditoidea:Steinemematidae, Heterorhanditidae) to the Asian longhorned beetle, Anoplophora glabripennis (Coleoptera:Cerambycidae)[J]. Biocontrol Sci Techno1, 2001, 11:547-552.

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通讯作者: 陈斌, bchen63@163.com

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沈阳化工大学材料科学与工程学院沈阳 110142

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Main environmental factors for forestry insects that become important pests

1. School of Forestry and Biotechnology, Zhejiang Forestry College, Lin'an 311300, Zhejiang, China;

2. Yuhang Ministry of Forest and Water Conservancy, Hangzhou 311100, Zhejiang, China

Received Date: 2006-11-14

Rev Recd Date: 2007-04-13

Key words:

Abstract: This paper discussed why some insects become pests with primary reasons being clarified in order to control pest of forest in the future. These reasons included drought, atmospheric pollution, consequences of global change, and exotic invasive species. Moreover, three key points for rationally allocating different tree species to forests, so as to prevent pest disasters, were put forward, namely:biodiversity to enhance ecosystem stability, a risk dispersing mechanism, and a relative resistance principle. Based on regulation of tree species distribution and time-space structure in forest ecological systems must either promote pest control or at least not increase forest pest damage.

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Reference (33)

[1]	HUGHES P R, CHIMENT J J, DICKIE A I, et al. Effect of pollutant dose on the response of Mexican bean beetle to SO₂-induced changes in soybean[J]. Env Ent, 1985, 14(6):718-721.
[2]	RIEMER J, WHITTAKER J B. Air pollution and insect herbivores:observed interactions and possible mechanisms[M]//Insect-Plant Interactions.Boca Raton:CRC,1989:73-105.
[3]	薛皎亮,谢映平,刘红霞.城市空气污染物SO₂和Pb在大球蚧及其寄主国槐体内积累的研究[J].林业科学, 1998, 34(1):45-49.
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[5]	ZVEREVA E L, KOZLOV M V. Effects of air pollution on natural enemies of the leaf beetle Melasoma lapponica[J]. J Appl Ecol, 2000, 37(2):298-308.
[6]	ZVEREVA E L, RANK N E. Host plant effects on parasitoid attack on the leaf beetle Chrysomela lapponica[J]. Oecologia, 2003, 135:258-267.
[7]	ZVEREVA E L, KOZLOV M V, HAUKIOJA E. Population dynamics of a herbivore in an industrially modified landscape:case study with Melasoma lapponica(Coleoptera:Chrysomelidae)[J]. Acta Phytopathol Entomol Hung, 1997, 32:251-258.
[8]	ZVEREVA E L, KOZLOV M V, NEUVONEN S. Decrease of feeding niche breadth of Melasoma lapponica(Coleoptera:Chrysomelidae) with increase of pollution[J]. Oecologia,1995,104:323-329.
[9]	ZVEREVA E L, KOZLOV M V, NEUVONEN S. Population density and performance of Melasoma lapponica(Coleoptera:Chrysomelidae) in surroundings of a smelter complex[J]. Environ Entomol, 1995, 24:707-715.
[10]	ZVEREVA E L, KOZLOV M V, NIEMELA P. Effects of leaf pubescence in Salix borealis on host-plant choice and feeding behaviour of the leaf beetle Melasoma lapponica[J]. Ent Exper Appl, 1998, 89:297-303.
[11]	ZVEREVA E L, KOZLOV M V, NIEMELA P, et al. Delayed induced resistance and increase in leaf fluctuating asymmetry as responses of Salix borealis to insect herbivory[J]. Oecologia, 1997, 109:368-373.
[12]	PIMENTEL D. Insect population response to environmental stress and pollutants[J]. Env Review, 1994, 2(1):1-5.
[13]	KOZLOV M V, NIEMELA P. Difference in needle length-a new and objective indicator of pollution impact on Scots pine (Pinus sylvestris)[J]. Water Air Soil Poll, 1999, 116:365-370.
[14]	KOZLOV M V, ZVEREVA E L, NIEMELA P. Shoot fluctuating asymmetry-a new and objective stress index in the Norway spruce (Picea abies)[J]. Can J For Res, 2001, 31:1289-1291.
[15]	KOZLOV M V, WILSEY B J, KORICHEVA J. Fluctuating asymmetry of birch leaves increases under pollution impact[J]. J Appl Ecol, 1996, 33:1489-1495.
[16]	PORT G R, THOMPSON J R. Outbreaks of insect herbivores on plants along motorways in the United Kingdom[J]. J Appl Eco, 1980, 17:649-656.
[17]	NEILSON R P, MARKS D. A global perspective of regional vegetation and hydrologic sensitivities from climatic change[J]. Veget Sci, 1994, 5:715-730.
[18]	SAIKKONEN K. Nuclear polyhedrosis virus of the European pine sawfly (Neodiprion sertifer) retains infectivity in soil treated with simulated acid rain[J]. J Appl Ent, 1995, 119(3):495-500.
[19]	NIELSEN J K, HANSEN M L, AGERBIRK N, et al. Responses of the flea beetles Phyllotreta nemorum and P. cruciferae to metabolically engineered Arabidopsis thaliana with an altered glucosinolate profile[J]. Chemoecology, 2001, 11:75-83.
[20]	MCINTOSH R L, ALLISON J D, et al. Comparative effcacy of five type of trap for woodborers in the Cerambycidae, Buprestidae and Siricidae[J]. Agric For Entomol, 2001, 3(2):113-120.
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[30]	SOLTER L F, KEENA M. Infectivity of four species of nematodes (Rhabditoidea:Steinemematidae, Heterorhanditidae) to the Asian longhorned beetle, Anoplophora glabripennis (Coleoptera:Cerambycidae)[J]. Biocontrol Sci Techno1, 2001, 11:547-552.
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Main environmental factors for forestry insects that become important pests

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通讯作者: 陈斌, bchen63@163.com

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