首页> 外文期刊>Silva lusitana >Predicting Defoliation by Pine Processionary Caterpillar, Thaumetopoea wilkinsoni (Lepidoptera: Notodontidae) in Young Pinus brutia Plantations in Northern Cyprus
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Predicting Defoliation by Pine Processionary Caterpillar, Thaumetopoea wilkinsoni (Lepidoptera: Notodontidae) in Young Pinus brutia Plantations in Northern Cyprus

机译:在北塞浦路斯的年轻松树人工林中,通过松散的毛毛虫毛毛虫(Thaumetopoea wilkinsoni(鳞翅目:Notodontidae)预测落叶)

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A method is described for predicting severity of defoliation of young Pinus brutia plantations ( 50% of the branches defoliated and/or larval colonies present This rating system provides a range of individual tree and plot ratings from 0 to 6 depending on the severity of defoliation. Results Timing of egg-mass surveys Initial screening of the data from sample plantations in which egg-mass surveys were conducted in early October had higher larval colony counts than egg-masses. Recounts of egg-mass numbers in these plantations during early December indicated that more egg masses were found in December. October egg-mass counts ranged from 33 to 94.2% of the egg masses found in December (Table 3). This discrepancy in egg-mass counts was believed to be the result of three possible scenarios: 1. October egg-mass surveys had been conducted before adult flight and oviposition were completed. 2. Egg-masses produce more than one larval colony. 3. Field crews did not detect all egg-masses present. Table 3 - Percentage of Pine Processionary Caterpillar Egg Masses Detected by First Egg-Mass Sample, Five-Finger Mountains, Northern Cyprus, 2002 If this discrepancy was due to egg-mass surveys being done before adult flight was completed, the greatest discrepancy between the two sets of egg-mass counts should have occurred in the low elevation plantations where adult flight and oviposition occurs later than at the high elevations (BUXTON, 1983). However, comparison of the proportion of egg-masses detected in October by elevation failed to show a clear trend (Table 4). It is, therefore, believed that the discrepancies between the October and December egg-mass counts are the result of all three factors listed earlier. Egg-mass counts taken in December were used in the analysis. Table 4 - Percent of Egg Masses Detected by First-Egg Mass Sample, by Elevation Zone, Five-Finger Mountains, Northern Cyprus, 2002 Data ranges The average number of egg-masses/tree for the 30 sample plantations ranged from a low of 0.20 to a high of 4.23. These were lower than the values obtained for the two plantations sampled in 2000. Larval colony densities per tree ranged from 0.20 to 4.49. Estimates of larval colonies were higher than estimates of egg-masses/tree in 11 of the sample plantations (Table 5). Table 5 - Distribution of Sample Plantations by Egg-Mass and Larval Densities, Five-Finger Mountains, Northern Cyprus, 2002 Estimates of precision Estimates of numbers of egg-mass densities per tree was within ± 0.5 egg-masses/ tree 95 out of 100 times in 25 out of the 30 sample plantations and within ±0.69 egg masses on the remaining sample plantations. This was considerably higher than the expected precision of ± 2 egg-masses 95 out of 100 times based on the data collected in 2000, especially considering that none of the sample plantations contained the recommended number of 50 sample trees. This is believed to be due to higher numbers of egg-masses on individual sample trees in 2000. One of the trees sampled in 2000 had 45 egg-masses (Table 1). This is probably unusual and adversely affected the estimate of sampling error. In 2002, the highest egg-mass count obtained on a single tree was 15. The precision of estimates of the numbers of larval colonies per tree was similar to the estimates of egg-mass densities. In 25 of the 30 sample plantations, estimates were within 0.5 larval colonies 95 out of 100 times. In the remaining five plantations, the estimate was within ±0.67 larval colonies/tree. Egg-mass/ Larval colony/ Defoliation correlations Regression analyses using the linear model y = a + bx (FREESE, 1978) was made for three relationships: 1. Egg masses/ tree (x) vs. early instar larval colonies/ tree (y) 2. Egg masses/ tree (x) vs. defoliation rating (y) 3. Early instar larval colonies/ tree (x) vs. defoliation rating (y) Each of these models showed a strong positive correlation between the dependent and independent variables with correlation coefficient
机译:描述了一种预测幼小松树人工林落叶的严重程度的方法(存在的落叶和/或幼虫菌落的分支的50%,该评级系统提供了从0到6的单个树和地块等级的范围,具体取决于结果卵子质量调查的时间安排初步筛选在10月初进行卵子质量调查的样本种植园中的数据,发现其幼虫菌落数高于卵子质量。表示12月份发现的鸡蛋量更多。10月份的鸡蛋质量数占12月份发现的鸡蛋质量的33%至94.2%(表3),这种鸡蛋数量的差异被认为是三个因素的结果。可能的情况:1.在成年飞行和产卵完成之前已进行了10月的卵量调查; 2.卵量产生了一个以上的幼虫菌落; 3.野外工作人员未检测到所有卵量。已发送。表3-2002年北塞浦路斯五手指山的第一个鸡蛋质量样本检测到的松树行进的毛毛虫卵质量百分比如果该差异是由于成年飞行完成之前进行的鸡蛋质量调查造成的,则两者之间的最大差异在成年飞行和产卵发生晚于高海拔的低海拔人工林中,应该有两组卵质量计数(BUXTON,1983)。但是,按海拔比较十月份检测到的鸡蛋质量的比例并没有显示出明显的趋势(表4)。因此,可以认为10月份和12月份的鸡蛋质量计数之间的差异是前面列出的所有三个因素的结果。分析中使用了12月份的鸡蛋质量计数。表4-2002年北塞浦路斯五指山高海拔地区通过首次鸡蛋质量样本检测到的鸡蛋质量百分比数据范围30个样本种植园的平均鸡蛋质量/树木数量在0.20的低点范围内达到4.23的高位。这些低于2000年采样的两个人工林获得的值。每棵树的幼虫菌落密度范围为0.20至4.49。在11个样本种植园中,幼虫菌落的估计数高于卵子质量/树木的估计数(表5)。表5-2002年北塞浦路斯五指山按鸡蛋质量和幼虫密度划分的人工林分布情况精确度估计每棵树的鸡蛋质量密度数在±0.5鸡蛋质量/每棵树中95于100在30个样本种植园中的25个中进行了两次定位,其余样本种植园的卵质量在±0.69以内。根据2000年收集的数据,这远高于100个样本中预期的±2个鸡蛋质量中的95个精度,特别是考虑到没有一个样本种植园包含建议数量的50个样本树。据信这是由于2000年单个样本树上的卵子数量增加。2000年抽样的其中一棵树有45个卵子质量(表1)。这可能是不寻常的,并且会对采样误差的估计产生不利影响。在2002年,在一棵树上获得的最高卵子质量数为15。每棵树的幼虫集落数的估计精度与卵子密度的估计值相似。在30个样本种植园中的25个中,估计有0.5个幼虫集落在100倍中的95个以内。在其余五个人工林中,估计的幼虫菌落/树在±0.67以内。卵量/幼虫菌落/落叶相关性使用线性模型y = a + bx(FREESE,1978)对以下三个关系进行回归分析:1.卵质量/树(x)与幼龄幼虫菌落/树(y )2.鸡蛋质量/树木(x)与脱叶等级(y)3.早期龄期幼虫菌落/树木(x)与脱叶等级(y)这些模型中的每一个都显示出因变量和自变量之间的正相关具有相关系数

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