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Title Why lacewings may fail to suppress aphids … Predators that eat other predators disrupt cotton aphid control
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Abstract Biological control of the cotton aphid involves complex interactions among predators now under study.

Authors
Rosenheim, Jay A.
Professor, Insect ecology, integrated pest management, and biological control. Use of farmer-generated data to enhance pest and crop management (Ecoinformatics)
Insect ecology, integrated pest management, and biological control. Use of farmer-generated data to enhance pest and crop management ('Ecoinformatics')
Wilhoit, Lawrence R. : L. R. Wilhoit was Postgraduate Researcher (currently an Environmental Research Scientist for the Department of Pesticide Regulation, California EPA), Department of Entomology, UC Davis
Publication Date Sep 1, 1993
Date Added May 27, 2009
Copyright © The Regents of the University of California
Copyright Year 1993
Description

The predatory green lacewing, Chrysoperla carnea, is often abundant in mid- and late-season cotton fields in the San Joaquin Valley. However, neither these natural populations nor insectary-reared and mass-released lace-wings appear to suppress populations of the cotton aphid. The key reason for the ineffectiveness of biological control appears to be the heavy mortality imposed on lacewing larvae by other generalist insect predators. Results of a study suggest that interactions between different species of insect predators may disrupt the biological control of pest species.

OCR Text
yield losses were apparent . As has been Why lacewings may fail to suppress aphids . . . found in studies of several different cot - ton insect pests , plants that are setting bolls appear to have limited abilities to compensate for feeding damage . During Predators that eat other the late season , when bolls are opening and cotton lint is exposed , cotton aphids create problems by excreting large quan - predators disrupt cotton tities of sugary honeydew , which fall onto lint and create â?? sticky cotton . â?쳌 Problems with sticky cotton become ap - aphid control parent during harvest , ginning and yarn manufacturing , and threaten overseas markets and the price premiums Califor - nia cotton has historically received . Be - Jay A . Rosenheim D Lawrence R . Wilhoit cause the cotton aphid is already resis - tant to many insecticides in California and an even larger array of pesticides in predators may attack other predators , the southern United States , long - term Thepredatory green lacewing , with potentially negative effects on pest management of aphids will probably Chrysoperla carnea , is often control . Here , we report a study de - need to rely on noninsecticidal alterna - abundant in mid - and late - season signed to determine the effectiveness of tives . lacewing larvae , Chrysoperla carnea , as cotton fields in the San Joaquin Cotton grown in the San Joaquin Val - biological control agents of the cotton ley generally develops large populations Valley . However , neither these aphid , Aphis gossypii , which feed on of generalist predators , including big - natural populations nor insecfary - mid - and late - season cotton in the San eyed bugs ( Geocoris spp . ) , damsel bugs reared and mass - released lace - Joaquin Valley . We found that a number ( Nabis spp . ) , assassin bugs ( Zelus spp . wings appear to suppress popula - of generalist predators impose heavy ( Orius and others ) , minute pirate bugs mortality on lacewing populations and of the cotton aphid . The key tions tristicolor ) and lacewings ( primarily thereby render natural and augmented Chrysoperla carnea ) . Other predators , less reason for the ineffectiveness of populations of lacewings ineffective as abundant , are also present . Lacewing biological control appears to be biological control agents . larvae , known as potential predators of the heavy mortality imposed on The cotton aphid , a major pest of cot - aphids in many crops , are available from lacewing larvae by other general - ton in California , presents very different several commercial insectaries . Some problems for cotton production at differ - ist insect predators . Results of a growers use augmentative releases of ent times of the year . Early season popu - purchased lacewings at the recom - study suggest that interactions lations , which develop on very small mended rate of 5,000 eggs per acre to between different species of in - cotton seedlings ( often on plants with improve control of cotton aphids . sect predators may disrupt the fewer than six nodes ) , can cause crinkled Natural densities of lacewings of pest species . biological control leaves , partial defoliation and stunted plant growth . Nevertheless , research still The first question addressed was : in progress suggests that this damage is How many lacewing eggs and larvae are fully compensated for before harvest naturally present in late - season cotton Rising costs of insecticides , widespread and that the timing of crop maturation , fields when sticky cotton is a potential insecticide resistance and increasing re - quantity of yield and cotton fiber quality problem ? Six fields were sampled be - strictions on insecticide use in California are unaffected . At mid - season , cotton tween August 26 and September 2,1992 . have spurred interest in insect manage - aphid populations are frequently low ; In each field , entire plants were sampled ment by other means , including biologi - however , during 1992 , populations in and carefully inspected to count all cal control . Generalist insect predators the southern San Joaquin Valley grew lacewings present . The number of plants are frequently abundant in annual crops , rapidly during July and August , and per row meter was recorded to translate including field and vegetable crops , and counts into lacewings per acre . As have been identified as important in shown in figure 1 , natural densities of suppressing populations of damaging lacewing eggs were in all cases high , insects . However , effective use of such ranging from 77,000 to 380,000 per acre . natural enemies to manage pests re - Clearly , these naturally present eggs quires more complete understanding of were so abundant in the sampled fields insect ecology , including the biology of that more releases of insectary - reared insect predators . lacewing eggs at the recommended rate In cotton , for instance , generalist ( 5,000 per acre ) would not be useful . Ob - predators may be critical in controlling servations of many other fields suggest populations of spider mites , Lygus bugs that lacewings establish large densities and several worm pests . Few pest man - Y - 5 of eggs in cotton fields at midseason and agement experts or insect ecologists 2 that these densities remain fairly stable have studied interactions between insect 5 for nearly all of the remainder of the predators , leaving the impression that P 7 growing season . Thus , before releasing insect predators feed exclusively on her - lacewings , sampling of naturally present Adults and nymphs of the cotton aphid , bivorous arthropods . However , it is pos - lacewings is recommended to determine Aphis gossypii . sible in theory that some generalist CALIFORNIA AGRICULTURE , SEPTEMBER - OCTOBER 1993 7 food limitation , was causing heavy mor - bugs , prey on lacewing larvae . Other predators that were abundant , for tality of young lacewing larvae . example damsel bugs , were never ob - Lacewing egg releases served feeding in the field on any prey ; thus , we were unable to determine if Methods . Experiments to assess the they preyed on lacewing larvae . To de - effect of lacewing egg releases were con - termine if generalist predators caused ducted at the Kearney Agricultural Cen - substantial mortality of lacewing larvae , ter and the UC Cotton Research Station and to quantify their effect on the bio - at Shafter in 1991 . Two treatments , the logical control of the cotton aphid , we release of 5,000 insectary - reared lace - performed a manipulative experiment . wing eggs and no eggs released , were Methods.This experiment , con - replicated ten times in a randomized ducted August 21 - 30 , 1992 , at the block design . Our release rate , about 260 Kearney Agricultural Center , was de - times the recommended rate of 5,000 signed to isolate the influences of each of eggs per acre , was chosen to determine three predators , big - eyed bugs , damsel whether any effect from lacewings could bugs and assassin bugs , with and with - be discerned ; smaller releases would out the presence of lacewings , on lace - have been dwarfed by naturally present wing survival and biological control of populations . Releases at these rates are not , however , commercially feasible . the cotton aphid . Individual plants har - Each plot was 10feet by 6 rows of cot - boring aphid populations were chosen ton , cultivar GC - 510 . Two days before for study . Each plant was carefully in - the lacewings were released and weekly spected to count all aphids and to re - thereafter , aphid densities in each plot move all nymphal and adult predators . were quantified by sampling ten leaves Polyester mesh sleeves were then per plot and counting all aphids . To de - placed over the plants to create a small termine the impact of the lacewings , we cage ( either the entire plant or the top portion of the plant was enclosed , de - used the ratio of postrelease aphid counts to prerelease aphid counts . pending on aphid density ) . Before seal - Results.Because the effects of the ing the sleeve cage , eight treatments , lacewing releases were similar in the each replicated 6 to 10 times , were then two experiments , the results are com - applied to the caged plants : ( 1 ) no pred - ators , an â?쳌 aphids only â?쳌 treatment ; bined in figure 2 . For 3 weeks following ( 2 ) the lacewing releases , aphid densities aphids plus two big - eyed bug adults ; remained approximately constant in the ( 3 ) aphids plus two damsel bug adults ; release plots but expanded in the non - ( 4 ) aphids plus two assassin bug adults ; ( 5 ) aphids plus five C . carnea lacewing release , control plots . By the second week , the aphid population in the re - lease plots was less than before release ( ratio = 0.85k 0.16 ) , while the aphid population had more than doubled in the control plots ( ratio = 2.37 & 0.67 ; t = 2.50 , P = 0.03 ) . This trend continued for a third week , but for the remaining period there was little or no difference between the two treatments ( fig . 2 ) . Thus , releases of extremely high densities of lacewing eggs produced only a modest and tran - sient suppression of aphid populations . We suspect that releases conducted at the recommended rate would not have produced detectable results . Fig . 1 . Naturally occurring densities of A few days after the lacewing eggs lacewing eggs and larvae in six fields were released , few lacewing larvae sampled during the late season ( August could be found in any of the plots . This - September 2,1992 ) in San Joaquin 26 Adult assassin bug , Zelus renardii . Assas - observation was consistent with many Valley cotton . Five plants were sampled in sin bugs were found to be major predators other observations where many adult each field except for field S1 , in which 48 of lacewing larvae . plants were sampled . Field K had been lacewings and their eggs were seen , but treated with methamidophos June 24 for few or no larvae were detected ( fig . 1 ) . Lygus control , and field S3 had been whether releases will substantially in - However , a number of other generalist treated with chlorpyrifos August 4 for crease densities in the field . predators were present . aphid control ; all other fields were never Although egg densities were uni - treated . Shown are means plus one stan - Predators attack lacewings formly high , in four of the six fields we dard error of the mean . No lacewing larvae recovered no lacewing larvae ( fig . I ) , de - Direct observations in the field in were recovered from fields WS1 , K , S2 spite the fact that in several of the fields 1991and 1992revealed that generalist S3 . WS = West Side Field Station ; K or cotton aphid prey were abundant . This predators , including nymphal big - eyed = Kearney Agricultural Center ; S = UC suggested that some factor , other than Cotton Research Station , Shafter . bugs and nymphal and adult assassin 8 CALIFORNIA AGRICULTURE , VOLUME 47 , NUMBER 5 when other predators were added . AI - logical control researchers . Densities of larvae ( second instar ) ; ( 6 ) aphids plus lacewing eggs are naturally high in San though big - eyed bugs had a minimal ef - five lacewing larvae plus two big - eyed Joaquin Valley cotton fields ; thus , aug - fect ( P = 0.15 ) , the addition of damsel bug adults ; ( 7 ) aphids plus five lacewing mentative releases of lacewings should bugs allowed aphid populations to start larvae plus two damsel bug adults ; ( 8 ) only be contemplated after field scout - growing again ( P = 0.01 ) , and the addi - aphids plus five lacewing larvae plus ing has shown that natural populations tion of assassin bugs appeared to re - two assassin bug adults . Lacewing lar - are not present in high densities . Our move most of the suppressive effect of vae were obtained from a commercial in - small plot releases suggest that releases sectary . After 7 to the lacewings 8 days , the plant ( P = 0.001 ; fig . 3b ) . of lacewing eggs at extremely high rates stems were cut and the sleeve cages Clearly , these predators did not act in an ( much higher than is commercially vi - brought into the laboratory , where all additive way to suppress aphid num - able given the cost of predators and aphids present were bers . Rather , the heavy predation by $ 3 to $ 4 per 1,000 eggs ) produced only modest suppres - counted . damsel bugs and assassin bugs on lacewing larvae allowed aphids to es - Results . Survival of lacewing larvae sion of aphids . Recommended release cape the effective biological control pro - varied strongly across the four treat - rates would probably not produce de - duced by the lacewings alone . This re - ments to which lacewings were added tectable results . The key reason why naturally present sult was surprising , especially for ( fig . 3a ) . Survival decreased from 47 % in the absence of predators to damsel bugs , which are known as major populations and augmentatively re - 20 % when predators of aphids . leased lacewing eggs do not control big - eyed bugs were present ( P = 0.06 ) , aphids appears to be the heavy mortality and to 0 % when either damsel bugs Conclusions imposed on lacewing larvae by other ( P = 0.001 ) or assassin bugs were generalist predators . Because our con - Biological control of the cotton aphid present ( P = 0.003 ) . We can infer that clusions are based on only the decreased lacewing survival was a 2 years of by generalist predators involves com - result of predation rather than competi - study , additional work is required to de - plex interactions among predators that termine how general our results are . We have not previously been studied by bio - tion for aphid prey , because the avail - ability of aphid prey was greater where need to understand fully the interactions between lacewings and other generalist predatory bugs were present . This nega - tive effect of the generalist predators on predators to predict late - season out - breaks of the cotton aphid . lacewing survival influenced the level of Can we manipulate this system to in - biological control of the cotton aphid crease the effectiveness of lacewings ? ( fig . 3b ) . The first five treatments shown We do not wish to suppress populations in figure 3b provide a test of whether of big - eyed bugs or damsel bugs because each of the four predators considered these predators probably help control alone has an impact on aphid population other cotton pests , including Lygus bugs , growth . When aphids were caged alone , their populations expanded rapidly , as spider mites and worms . Thus , we may need to search for other biological con - expected . Assassin bugs and big - eyed bugs alone exerted minimal influences trol agents for the cotton aphid that are on the rate of aphid population growth not susceptible to these predators , or de - velop other control tactics , such as host ( P > 0.10 ) . Damsel bugs slowed aphid plant resistance or cultural techniques . = 0.03 ) , population growth substantially ( P Research continues on all of these fronts . but did not control the populations . Lace - wing larvae were , however , able to cause aphid populations to decrease rather than expand P = 0.001 ) ; the me - 1 . A . Rosenheim is Assistant Professor and L . R . Wilhoit was Postgraduate Researcher dian response was a 91.2 % decrease of aphid numbers . ( currently an Environmental Research Scientist for the Department of Pesticide This highly successful level of bio - Regulation , California EPA ) , Department logical control produced by lacewing of Entomology , UC Davis . larvae feeding alone was disrupted The authors thank Christine Armer and Paul Wynholdsfor technical assistance ; Thomas Leighfor the use offield cages ; Kent Les Ehler and Thomas Leighfor Daane , helpful discussions ; and Sinthya Penn and William Lalorfor comments on this manu - script . They thank the staffof the Kearney Agricultural Center and the UC Cotton Re - search Station , Shafler , for growing the experi - mental cotton plantings , and the Rincon - Fig . 3 . Influences of generalist predators yfor providing lacewing eggs Vitoua lnsecta ( B ) per - on ( A ) lacewing larval survival and for testing . capita aphid population growth rates . Per - This study wasfunded by cotton - grower capita aphid population growth was calcu - funds made available through Cotton lncor - - initial lated as ( final aphid numbers porated , in cooperation with the California aphid numbers ) / ( initial aphid numbers ) ; a Fig . 2 . Field experiment assessing the State Support Committee , Rick Wegis , value of 0.0 indicates no change in aphid efficacy of augmentative releases of green chairman , and the University of California populations . Aphids were present in all lacewing eggs for biological control of the treatments . cotton aphid . Statewide lPM Project . CALIFORNIA AGRICULTURE , SEPTEMBER - OCTOBER 1993 9
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