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Biology and Management of Amur honeysuckle (Lonicera maackii)
R.J. Smeda,
S.A. Riley
• Lonicera spp. are known as honeysuckles and are comprised of vining perennials and shrubs
• Grape honeysuckle (Lonicera reticulata) is an example of a native vining honeysuckle
• This vine can grow up to 4.5 meters and prefers to grow up existing vegetation
MDC (2013)
INTRODUCTION
• Invasive bush honeysuckles are a group composed of 4 species– Amur
– Morrow’s
– Tartarian
– Belle’s(Vermont 1998)
• Stems of invasive shrubs are hollow which is distinguishable from native solid-stemmed honeysuckles
• Amur honeysuckle was introduced to the
U.S. in the late 1800s(Dirr 1983)
• Its invasion has been widespread
because seeds are vectored by birds
(Luken 1988)
www.invasive.org
• Amur honeysuckle is
common throughout
Missouri
• Prefers partially shaded
habitats:
– treelines,
– fencerows
– other undisturbed areas
• Reproduction is by seed only
• Berries contain from 3 to 8 seeds
• Shrubs produce thousands of berries each season
• Berries are eaten by birds and seeds dispersed
www.hiltonpond.org
www.ohionatureblog.com
• Shrubs form a
dense thicket that
may displace
desirable understory
species due to light
inhibition and
allelopathic effects
• Amur honeysuckle
can reach 6 m in
height
• Plants in MO initiate
growth in April and
retain leaves into
December
Infestated areas are quite visible following first snow events
December 8
Amur honeysuckle is an urban and rural problem Columbia Missourian
September 16, 2011
The St. Louis Audubon Society currently supports efforts to eradicateinfestations
Outline
• Study 1: Seed Biology
– Seed viability through time
– Berry counts
– Bird predation through time
• Study 2: Herbicide Trial
– Herbicides for brush control
– Response of Amur honeysuckle to herbicides
M.S. research of S.A. Riley
jimmccormac.blogspot.com
forestrenewal.blogspot.com
Objective: Seed Biology• Assess timing for maturity of Amur honeysuckle
seeds
• Estimate seed production capacity
• Determine reduction in berry population on shrubs as seeds reached maturity
Tetrazolium Assay
• Exposure of seeds to a tetrazolium solution is an accepted way to assess viability
• Actively respiring tissues are stained red by the TZ solution
• Non-respiring tissues are not stained
• For Amur honeysuckle all internal tissues of seeds must be stained for positive viability assessment
Methodology - tetrazolium
• Berries (20) dissected for seed harvest at different times for 2 MO locations (2011 and 2012)
• Seeds immersed in water overnight to facilitate dissection
• Seeds were dissected and distal end was place in 1% TZ solution overnight at 35 C in a temperature controlled chamber
• Seeds were dissected and viability assessed Distal
Basal
1st Cut
2nd Cut
Staining pattern
Nonviable
Viable
40X
Harvest Timing Viability (%)
Early-September 0 da
Mid-September 22 c
Late-September 61 b
Mid-October 83 ab
Late-October 86 a
Early-November 90 a
a Means within each column followed by the same letter are not significantly different using Fisher’sProtected LSD at P=0.05
• No seed viability detected until mid-September• Maximum viability reached in early-November
Results:
Methodology for seed production:
• 50 random berries harvested and seeds extracted and counted
• Over 4 site years, bird netting placed over shrubs and weed block placed beneath shrubs
• All berries counted in October on 5 random shrubs per site year (4)
Amur honeysuckle seed production per shrub in Missouri
Location Total berry # Seeds per berry
Total seed production
Ashland, 2011 1,554 (+ 366)ab 2.8 (+ 0.1) a 4,477 (+ 1174)
Columbia, 2011 2,067 (+ 633) 3.3 (+ 0.1) a 7,161 (+ 2378)
Ashland, 2012 3,172 (+ 637) 1.0 (+ 0.2) b 3,150 (+ 1034)
Columbia, 2012 4,173 (+ 1927) 0.7 (+ 0.1) b 2,844 (+ 1031)
aNumber in parentheses indicates the standard error of the mean.bMeans within each column followed by the same letter or without letters not significantly different using Fisher’s Protected LSD at P=0.05.
• Netting and weed mat was placed beneath shrubs to prevent predation of fallen fruits
• Initial berry counts were taken in late September each year until all berries disappeared
• Additional counts of 4 shrubs at 2 locations were taken every 15 days
• Experiment was a randomized complete block with 4 replications; data generated for 4 site years
Methodology for berry predation
Means not followed by the same letter for each curve not significantly different using Fisher’s Protected LSD at P=0.05.
• 83% viability was observed by mid-October
• 250 berries per week were lost due to predation from October through December
• Large numbers of viable seed are dispersed through the winter months
Objective: Herbicide Study
• Determine herbicide efficacy on Amur
honeysuckle using foliar (summer)
applications
newyorkinvasivespecies.info
Materials and Methods
Foliar Applications
• Two locations: Columbia and Moberly, MO in 2011; Ashland and Columbia, MO in 2012
• Amur honeysuckle was mowed in fall of 2010 and 2011 with shrubs allowed to re-grow to 1 meter before treating
• Applications were made on June 27 and July 8, 2011 and July 9 and 18, 2012
TreatmentsChemical Rate (g ae/ha) Surfactant
Glyphosate 1577 3.36 kg/ha AMS
2,4-D 1317.6 0.25% V/V NIS
2,4-D + Dicamba + Fluroxypyr 785 + 98.1 + 98.1 -
Triclopyr + Imazapyr 3 %v/v + 0.125%v/v 1% V/V MSO
Picloram + Fluroxypyr 375.3 + 302.8 0.5% V/V NIS
Sulfometuron + Metsulfuron 69 + 18.4* 0.25% V/V NIS
Triclopyr + Fluroxypyr 578.2 + 192.7 1% V/V NIS
Aminocyclopyrachlor +
Metsulfuron131.5 + 41.9* 0.5% V/V MSO
Aminocyclopyrachlor +
Metsulfuron + Imazapyr271.4 + 87 + 376.8* 0.5% V/V MSO
*g ai/ha
• Applications made with
a CO2 pressurized
backpack sprayer at 374
L ha-1 using TeeJet XR
8002 nozzle tips
• Plots were 2 by 7.6 m
• Visual ratings of
honeysuckle injury (0 =
no control, 100 = plant
death) at 28, 90, and
120 days after treatment
(DAT)
• Experimental design
was a randomized
complete block with 5
replications at each
location
Visual Control Examples
100%50%0%
Results Foliar applications
28 DAT; % Visual control
2011
Glyphosa
te2,4
-D
2,4-D
+ D
icam
ba + F
luroxy
pyr
Triclopyr
+ Im
azapyr
Piclora
m +
FLuro
xypyr
Sufom
eturo
n + M
etsulfu
ron
Triclopyr
+ F
luroxy
pyr
Aminopch
lor + M
etsulfu
ron
Aminopch
lor + M
etsulfu
ron +
Imaza
pyr0
20
40
60
80
100
Moberly LSD=17
Columbia LSD=17
2012
Glyphosa
te2,4
-D
2,4-D
+ D
icam
ba + F
luroxy
pyr
Triclopyr
+ Im
azapyr
Piclora
m +
FLuro
xypyr
Sufom
eturo
n + M
etsulfu
ron
Triclopyr
+ F
luroxy
pyr
Aminopch
lor + M
etsulfu
ron
Aminopch
lor + M
etsulfu
ron +
Imaza
pyr0
20
40
60
80
100
Moberly LSD=17
Ashland LSD=13
• Acceptable control by industry standards is 90% or greater
• Several herbicides exhibited >80% control by 28 DAT:
– aminocyclopyrachlor + metsulfuron + imazapyr
– aminocyclopyrachlor + metsulfuron
– glyphosate
90 DAT; % Visual control
2011
Glyphosa
te2,4
-D
2,4-D
+ D
icam
ba + F
luroxy
pyr
Triclopyr
+ Im
azapyr
Piclora
m +
FLuro
xypyr
Sufom
eturo
n + M
etsulfu
ron
Triclopyr
+ F
luroxy
pyr
Aminopch
lor + M
etsulfu
ron
Aminopch
lor + M
etsulfu
ron +
Imaza
pyr0
20
40
60
80
100
Moberly LSD=20
Columbia LSD=17
2012
Glyphosa
te2,4
-D
2,4-D
+ D
icam
ba + F
luroxy
pyr
Triclopyr
+ Im
azapyr
Piclora
m +
FLuro
xypyr
Sufom
eturo
n + M
etsulfu
ron
Triclopyr
+ F
luroxy
pyr
Aminopch
lor + M
etsulfu
ron
Aminopch
lor + M
etsulfu
ron +
Imaza
pyr0
20
40
60
80
100
Moberly LSD=21
Ashland LSD=17
120 DAT; % Visual control
2011
Glyphosa
te2,4
-D
2,4-D
+ D
icam
ba + F
luroxy
pyr
Triclopyr
+ Im
azapyr
Piclora
m +
FLuro
xypyr
Sufom
eturo
n + M
etsulfu
ron
Triclopyr
+ F
luroxy
pyr
Aminopch
lor + M
etsulfu
ron
Aminopch
lor + M
etsulfu
ron +
Imaza
pyr0
20
40
60
80
100
Moberly LSD=18
Columbia LSD=14
2012
Glyphosa
te2,4
-D
2,4-D
+ D
icam
ba + F
luroxy
pyr
Triclopyr
+ Im
azapyr
Piclora
m +
FLuro
xypyr
Sufom
eturo
n + M
etsulfu
ron
Triclopyr
+ F
luroxy
pyr
Aminopch
lor + M
etsulfu
ron
Aminopch
lor + M
etsulfu
ron +
Imaza
pyr0
20
40
60
80
100
Moberly LSD=18
Ashland LSD=13
120 DAT
Untreated Glyphosate
120 DAT
2,4-DAminocyclopyrachlor + Metsulfuron
+ Imazapyr
• Control of Amur honeysuckle had greatly improved by 90 and 120 DAT from 28 DAT.
• Best treatments across site years were:
– aminocyclopyrachlor + metsulfuron + imazapyr
– aminocyclopyrachlor + metsulfuron
– glyphosate
Conclusions
• Amur honeysuckle seeds are viable by mid-October
• Large numbers of viable seeds are dispersed every winter through bird predation
• Control of this shrub can be achieved with a summer application of an aminocyclopyrachlor containing herbicide or glyphosate.
• We can only stop the spread of infestations by preventing berry production
Questions?