JOURNAL OF NANJING FORESTRY UNIVERSITY ›› 2020, Vol. 44 ›› Issue (1): 125-130.doi: 10.3969/j.issn.1000-2006.201811019
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CHENG Qiang(), WU Xiaoqin*(), YE Jianren, LIN Sixi
Received:
2018-11-10
Revised:
2019-08-31
Online:
2020-02-08
Published:
2020-02-02
Contact:
WU Xiaoqin
E-mail:1422968941@qq.com;xqwu@njfu.edu.cn
CLC Number:
CHENG Qiang, WU Xiaoqin, YE Jianren, LIN Sixi. Distribution of Corythucha marmorata in Nanjing and its risk analysis in China[J]. JOURNAL OF NANJING FORESTRY UNIVERSITY, 2020, 44(1): 125-130.
Table 1
Distribution and hazard of Corythucha marmorata in Nanjing in 2018 "
序号 No. | 调查点 site | 区名 district name | 寄主 host plant | 寄主性质 host’s nature | 危害程度 damage degree |
---|---|---|---|---|---|
1 | 四方新村 | 秦淮区 | 菊花 | 自栽品种 | + |
2 | 晨光路绿化带 | 秦淮区 | 一枝黄花 | 野生杂草 | + |
3 | 和平广场花圃 | 建邺区 | 菊花 | 自栽品种 | + |
4 | 莫愁湖西门公交站 | 建邺区 | 菊花 | 自栽品种 | + |
5 | 湖西桥绿地 | 建邺区 | 一枝黄花 | 野生杂草 | ++ |
6 | 庐山路绿化带 | 建邺区 | 一枝黄花 | 野生杂草 | + |
7 | 碧瑶花园 | 建邺区 | 一枝黄花 | 野生杂草 | + |
8 | 河西中央公园 | 建邺区 | 一枝黄花 | 野生杂草 | + |
9 | 金沙江东街绿化带 | 建邺区 | 一枝黄花 | 野生杂草 | + |
10 | 江东南路绿化带 | 建邺区 | 小蓬草 | 野生杂草 | +++ |
11 | 雨花台风景区 | 雨花台区 | 香丝草 | 野生杂草 | + |
12 | 菊花台公园公交站 | 雨花台区 | 小蓬草 | 野生杂草 | +++ |
13 | 小行路绿化带 | 雨花台区 | 小蓬草 | 野生杂草 | + |
14 | 雨花东路绿地 | 雨花台区 | 春飞蓬 | 野生杂草 | + |
15 | 岔琥路绿化带 | 浦口区 | 一枝黄花 | 野生杂草 | + |
16 | 老山森林公园 | 浦口区 | 一枝黄花、春飞蓬 | 野生杂草 | ++ |
17 | 七乡河大道绿化带 | 栖霞区 | 一年蓬、一枝黄花 | 野生杂草 | ++ |
18 | 羊山公园 | 栖霞区 | 一枝黄花 | 野生杂草 | + |
19 | 玄武大道绿化带 | 玄武区 | 一枝黄花、春飞蓬 | 野生杂草 | ++ |
20 | 南京林业大学绿地 | 玄武区 | 一枝黄花、春飞蓬 | 野生杂草 | + |
21 | 云栖山庄 | 江宁区 | 一枝黄花 | 野生杂草 | +++ |
Table 2
The index layer evaluation of integrated multi index evaluation system for Corythucha marmorata "
目标层 objective | 准则层Pi criterion layer | 指标层Pij index layer | 赋分值 score | 评价赋分理由 evaluation reference |
---|---|---|---|---|
有害生物 风险综合 评价值R integrqated assessment value of pest (R) | 传入 可能性P1 possibility of introduced (P1) | 国内分布情况P11 | 2 | 国内分布面积占0~20%。目前国内已知上海、浙江慈溪、江苏南京、湖北武汉、河南信阳、台湾、江西赣州有分布[ |
国外分布情况P12 | 1 | 0~20%的国家有分布。国外报道北美、韩国、日本有分布[ | ||
有害生物运输过程中 的存活率P13 | 2 | 存活率在10%~40%。菊方翅网蝽可随沿途交通运输和菊科花卉品种的异地引种远距离传播,运输过程中存活率较高[ | ||
受害寄主的分布范围 或面积P14 | 2 | 寄主分布面积中等。受害寄主在我国分布广泛,如甘薯、加拿大一枝黄花、小蓬草、向日葵、菊芋、菊花等[ | ||
有害生物被调运 的可能性P15 | 2 | 被调运和携带繁殖体的可能性为20%~50%。菊方翅网蝽随交通运输工具、花卉引种调运的可能性大[ | ||
定殖 可能性P2 possibility of colonization (P2) | 有害生物生物学 特性P21 | 2 | 抗逆性弱,繁殖能力强(逆境条件下存活率0~50%,繁殖量大,年繁殖世代2~4代)。菊方翅网蝽繁殖力强,武汉一年繁殖5代[ | |
国内具备适宜定殖条件 的地区P22 | 2 | 国内20%~50%的地区具备其定殖的条件。我国地域辽阔,横跨5个气候带,气候类型多样,与菊方翅网蝽原产地北美洲气候类型相似;并且寄主在我国广泛分布,为其定殖提供了场所和食物来源[ | ||
扩散 可能性P3 possibility of spread (P3) | 可能存在的传播途径P31 | 2 | 3~5种传播途径。昆虫的自然迁飞;随交通工具、苗木引种、集装箱等方式进行远距离传播[ | |
国内的适生范围P32 | 2 | 国内的适生范围25%~50% | ||
天敌存在的可能性P33 | 3 | 本地区不存在有效的天敌 | ||
目标层 objective | 准则层Pi criterion layer | 指标层Pij index layer | 赋分值 score | 评价赋分理由 evaluation reference |
有害生物 风险综合 评价值R integrated assessment value of pest (R) | 受害寄主 经济重要性P4 economic importance of the hosts (P4) | 寄主的种类P41 | 3 | 受害的栽培寄主达10种以上。危害勋章菊(Azania rigens)、魁蒿(Artemisia princeps)、菊芋、紫背天葵(Gynura bicolor)、金光菊(Rudbeckia serotina)、蓝刺头(Echinops sphaerocephalus)、甘薯、向日葵、菊花、紫苑(Aster sp.)等多种植物[ |
寄主的潜在 损失水平P42 | 3 | 传入可造成的寄主植物死亡率或产量损失≥20%。菊方翅网蝽可危害向日葵和甘薯,使其产量降低;此外还能危害菊花,大大降低其观赏价值[ | ||
国外重视程度P43 | 0 | 未重视,0个国家将其列为检疫性有害生物 | ||
是否为其他检疫性 有害生物的传播媒介P44 | 0 | 不传带任何检疫性有害生物 | ||
危险性 管理难度P5 obstacles in the risk management (P5) | 非经济方面的 潜在损失P45 | 3 | 防治手段和有害生物本身都对生态和社会资源造成严重损害。菊方翅网蝽可危害多种寄主,给生态造成严重危害;化学防治可能会造成环境污染[ | |
检疫识别难度P51 | 2 | 当场鉴定可靠性一般,由经过专业培训的人员才能识别[ | ||
除害处理难度P52 | 1 | 除害率50%~100%。啶虫脒、联苯菊酯、毒死蜱等化学药剂效果显著,除害率>80%[ | ||
根除难度P53 | 2 | 防效高,但方法复杂、难度大、成本高。啶虫脒、联苯菊酯、毒死蜱等化学药剂效果显著。但该虫寄主分布广泛,野外条件复杂,加大了根除难度。且化学防治易造成环境污染[ | ||
R | 2.05 |
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