NCS000593_Emails RE UFP Facilities MCA_20200528

Georgoulias, Bethany
From: Moore, James
Sent: Thursday, May 28, 2020 7:02 PM
To: Lucas, Annette; Georgoulias, Bethany; Khan, Zahid
Subject: FW: [External] UFP Facilities
Attachments: Review of Copper -Based Wood Preservatives.pdf
Please see attached from UFP, follow up to letter he wrote earlier this month. At this point I am going to acknowledge
that he has initiated action under Tier 2/3 evaluating for sources of copper and follow up with a TA site inspection when
he is able to travel from Michigan.
From: Joe Mark [mailto:[e-mail]]
Sent: Thursday, May 28, 2020 4:22 PM
To: Moore, James <[e-mail]>
Subject: [External] UFP Facilities
External email. Do not click links or open attachments unless you verify. Send all suspicious email as an attachment to
[e-mail]
James
Thank you for your time yesterday.
Attached is a copy of the paper I mentioned during our conversation.
UFP facilities use Micronized Copper Azole (MCA) suspension when pressure treating wood. Copper carbonate which has
been pulverized into nanoparticles is forced under pressure through pores in the cell walls of the wood. The copper is
not dissolved in solution. No CCA is used at either of the Rowan County facilities.
You visited the UFP Salisbury facility in September 2017 as part of the storm water permit renewal process for that
facility.
I don't believe you have visited our other facility in Rowan county.
Both of these facilities are under individual storm water permits.
I was incorrect yesterday when I said both facilities were under the generic storm water permit.
As the COVID-19 situation winds down I will be contacting you to request Technical Assistance Inspections to help us
comply with our Tier 2 obligations.
Please contact me if you have any questions or require additional information on this matter.
Due to COVID-19 restrictions I'm in the office between 7 AM and noon eastern time.
After noon, I am working remotely and can be reached on my cell at [phone].

Joe Mark, CPG, RG
Regulatory Compliance Administrator
9),UFP INDUSTRIES
2801 East Beltline Ave. NE
Grand Rapids, MI 49525
Phone: [phone]
Cisco: 200-1591

By Mike H. Freeman* and Craig R. McIntyre*
Abstract
This paper focuses on the wood preservation aspects of copper based biocides.
Included in this review are the following: Above ground and ground contact
efficacy, permanence in above ground and ground contact uses, soil and
water contact leaching, effects on wood properties and certain fixation
aspects of copper systems. Previously unpublished data on the new
micronized/dispersed copper based wood preservative systems are also
included. These micronized systems now dominate the U.S. residential treated
wood market which in turn accounts for roughly 50 percent of global wood
preservation usage.
opper is an essential micronutrient for most living
cells. In larger doses though, the copper ion demon-
strates activity as an algaecide, bactericide, fungi-
cide, insecticide, and moldicide. Presently copper com-
pounds are used for algal control, wood treatment,
antifouling pigments, and crop fungicides (Richardson
1997). The fungicidal properties of copper were recog-
nized in the 1700s, and copper -based preservatives have
been widely and successfully used for more than a centu-
ry. Although borates and organic biocides are gaining
importance, copper remains the primary biocide compo-
nent used today to protect wood used in ground contact
or fully exposed to the weather (Lebow et al. 2004).
Copper is needed against this challenge since very few
organic molecules (other than creosote and penta) possess
activity towards soft rot fungi (Hughes 2004).
The volume of wood products treated with copper -based
preservatives grew exponentially during the 1970s and
1980s and remains high today. Copper compounds also have
This paper was received for publication in August 2008 and has
undergone the Journal's peer review process. Article No. 10523
Forest Products Society Member
© Forest Products Society 2008
Forest Prod. J. 58(11): 6-27
6 NOVEMBER 2008

advantages: it is relatively easy to create waterborne formula-
tions; it is easy to analyze and determine penetration in wood,
and copper slows photodegradation by UV radiation and
water (Archer and Preston 2006). The focus on copper -based
preservatives has increased following concerns about environ-
mental effects of chromium and arsenic and resulting restric-
tions on the use of chromated copper arsenate (CCA). Much of
the early work on copper -based formulations forms the basis
for the ammoniacal and amine copper -based systems current-
ly in the marketplace as CCA replacements (Preston et al.
1985). These formulations include quats or azoles as co -bio-
cides. Recently micronized copper formulations with the same
co -biocides have come into use. The drawbacks on use of cop-
per compounds include: copper tolerance exhibited in a num-
ber of fungal species, possible corrosivity to metal fasteners
and aquatic toxicity (Archer and Preston 2006). This paper
presents a discussion on copper issues such as the mode of
action, problems of copper tolerance, replacements for CCA,
the latest micronized formulations and environmental effects
of copper -based preservatives.
Mode of action of copper
The initial uptake of copper in cells is most likely by ion -
exchange followed by permeation throughout the cell
(Somers 1963). Copper is accumulated passively in fungal
spores by unspecific reactions with cell constituents. High lev-
els of copper uptake are required for fungicidal action in fungi,
and it is suggested that there are different sites of action for
the fungistatic and fungicidal processes (Somers 1963).
Increased copper uptake by spores is observed under anaer-
obic conditions and with temperature increase. At 35 °C,
uptake is almost three times that at 4 °C. The distribution of
accumulated copper in spores varies with fungal species and
fungal cell walls have a varying affinity for copper. The fungi-
cidal property of copper is dependent on its affinity to differ-
ent groups on fungal proteins, particularly thiol groups.
Excess copper causes damage by oxidizing proteins,
enzymes, lipids and therefore interrupting enzymatic process-
es (Eaton and Hale 1993, Rui and Morrell 1994). Copper also
inhibits intracellular enzymes responsible for destruction of
lignocellulosic materials, binds to the cell wall and interrupts
the transport of nutrients into and out of the cell. If enough
copper enters the cell, it can lead to denaturation of proteins
and enzymes leading to cell death (Archer and Preston 2006).
One specific mechanism proposed is the interaction
Of CuZ' with hydrogen peroxide, which results in reduction
to Cu' and production of free radicals from hydrogen per-
oxide and oxygen. Free radicals result in an uncontrolled
oxidation process via the Haber -Weiss cycle (Simpson et
al. 1988, Gunther et al. 1995). In aqueous solution the Cu'
derivatives are readily oxidized to CuZ'.
Copper toxicity can be suppressed by limiting its bio-
logical availability through complexation or precipitation
with proteins or metal chelating agents, e.g., ethylene-
diamine-tetra-acetic acid (EDTA). Copper toxicity may also
be reduced in some copper tolerant fungal species in pres-
ence of a nitrogen source, e.g., increased ammonia in alka-
line copper quaternary (ACQ), and this is attributed to
stimulation of oxalic acid production (Ruddick and Xie
1994, Humar et al. 2005).
Tolerance and copper
induced fungal secretions
The ability of some fungi to decay wood is stimulated
by low levels of copper in the wood. Compared with other
microbes, fungi can be extremely tolerant of toxic metals
at high concentrations. Several brown -rot wood decay
fungi in the genera Serpula and some species that were
once included within the genus Poria are tolerant of cop-
per (De Groot and Woodward 1999). Since copper is the
Copper -treated wood is widely used in
residential applications.
FOREST PRODUCTS JOURNAL VOL. 58, No. 1 1 7

most frequently used biocide for wood preservation, a
major requirement of any formulation of copper -based
wood preservative is efficacy against copper -tolerant fungi
(Nicholas and Schultz 1997). Renewed interest and concern
about the capability of certain fungi to decay wood treated
with copper preservatives stemmed from the voluntary
2004 withdrawal from residential applications of wood
treated with CCA. The arsenic in CCA effectively controlled
copper tolerant fungi (Steenkjwr Hastrup et al. 2005).
Microbes possess a range of tolerance mechanisms,
most featuring some kind of detoxification. Copper toler-
ance has been ascribed to diverse mechanisms involving
trapping of the metal by cell -wall components, altered
uptake of copper when the plasma membrane of mycelium
is less permeable to copper, extracellular chelation or pre-
cipitation by secreted metabolites and intracellular com-
plexing by metallothioneins and phytochelatins
(Cervantes and Gutierrez -Corona 1994). If a substance
which binds and detoxifies a metal has a significant pres-
ence, the metal content of the mycelium may be high even
if permeability to the metal is not.
Considerable work has been done regarding fungal abil-
ity to immobilize copper by precipitating copper oxalate
crystals around the hyphae (Sutter et al. 1983, Murphy and
Table 1. - Summary of copper -containing formulations and AWPA
retentions.
Preservative Co -biocide AWPA Retention m3
Above ground
Ground Contact
(UC1-UC3B)
UC4A
UC4B
ACC
4.0
8.0
ACQ-A, B, D DDAC or DDA-Carb
4.0
6.4
9.6
ACQ- C ADBAC
4.0
6.4
9.6
ACZA Zinc, Arsenic
4.0
6.4
9.6
CCA-C Arsenic
4.0
6.4
9.6
Copper Azole (CA-B) Triazole
1.7
3.3
5.0
Copper HDO (CX-A) HDO, boric acid
3.3
-
-
CuNap-Water Borne
l.la
1.8-
-
CuNap-Oil Borne
0.6a
1.0 - 2.4a,b
-
-
Oxine Cu-Oil Borne
0.11
a Copper as metal
b Retentions vary based on species and use
Table 2. - Summary of ICC-ES retentions.
Company System
Arch
CA-C
1.0
2.4
Arch
Micro CAa
0.8
2.2
Osmose
ACQ
3.2
6.4
Osmose
Micro CA
1.0
2.4
Osmose
Micro CQa
2.4
5.4
PhibroWood
Micro CA
1.1
2.6
Viance
ACQ
2.4
6.4
Dr. Wolman (BASF)
CX-A
3.3
4.8
aMicronized formulations -see text for explanation
Levy 1983). Copper tolerance has been linked to oxalic acid
producing species such as WoMporia cocos and Poria pla-
centa (Sutter et al. 1983, Clausen et al. 2000, Woodward and
De Groot 1999). A reduction of the toxicity of copper with
increased acidity has been observed in several fungi. The
presence of copper in waterborne preservatives ACQ, cop-
per citrate (CC), and CCA has been shown to stimulate pro-
duction of 66 to 93 percent more oxalic acid compared to
untreated controls within 2 weeks of exposure of blocks to
test fungi (Clausen and Green 2003). Calcium oxalate and
copper oxalate crystals are commonly observed in decayed
wood that has been treated with copper -based preserva-
tives. Choi et al (2002) demonstrated that copper prevents
germination of the spores of copper -tolerant fungi since
spores are not actively producing oxalic acid. Consequently,
preservatives containing copper without an effective co -
biocide can provide good performance when there is no
likelihood of attack by fungus mycelium.
The relative tolerance of fungal strains to copper -con-
taining preservatives varies with the formulation of the pre-
servative. Oxine copper offers excellent protection against
decay fungi including copper -tolerant fungi. In contrast to
the stimulated production of oxalic acid by ACQ, CC, and
CCA, oxine copper has been shown to prevent oxalic acid
production and weight loss by P. placenta, W. Cocos,
Meruliporia incrassata, and Antrodia vaillantii.
(Clausen and Green 2003). Studies using copper
naphthenate did not give a similar performance as
oxine copper (Sutter et al 1983) SimilarlYthe
• �
same strains of S. lacrymans used in agar plate
assays against CCA and in agar block tests
against copper naphthenate (CuNap) showed a
difference in relative tolerance of the isolates
against the two preservatives (De Groot and
Woodward 1999). Sutter et al. (1983) postulated
that the oil component in CuNap and oxine cop-
per physically prevents movement of precipitat-
ed copper oxalate to the exterior of the wood
surface. Morrell (1991) commented that copper
naphthenate would perform well in temperate
regions since attack has only been noted in
Florida even though copper -tolerant fungi are
seemingly widespread. Variation with CC was
also observed in that 11 of 12 isolates of S. lacry-
mans were tolerant towards CC because it
induced high levels of oxalic acid early in the
decay process (Sutter et al. 1983). As a result, CC
is often used in laboratory studies on copper-tol-
Itact erant fungi where the presence of co -biocides,
I4B such as chromium and arsenic, could confound
4.0 the results (De Groot and Woodward 1999).
3.6 Fungal reactions triggered by the presence
9.6 of copper include the formation of a thicker cell
3.7 wall and increased proportion of extracellular
9.6 mucilaginous material (ECMM). Vesentini et al.
3.8 (2006a) exposed copper -treated Scots pine
9.6 blocks to Coriolus versicolor and Gloeophyllum
7.2 trabeum and observed an increase in N-acetyl
glucosamine in fungal mycelium. The amount of
N-acetyl glucosamine is correlated with the
amount of chitin present (Nilsson and Bjurman
8 NOVEMBER2008

1998). The increase of chitin deposition in fungal cell wall
is related to the development of a thick cell wall.
Increasing the copper concentration in Trametes versicolor
culture media results in a decrease in the length of mycelia
peripheral growth unit (PGU) and to the increased propor-
tion of ECMM (Vesentini et al. 2006b). Both decreased PGU
and increased proportion of ECMM increase tolerance in
fungi to copper.
Copper -containing systems
In recent years, several preservative formulations
have been standardized by the American Wood Protection
Association (AWPA) for use in applications previously
dominated by CCA. The alternatives all center on copper
as their primary active ingredient but include inorganic or
organic co -biocides instead of chromium and arsenic. The
first commercial copper preservatives were based on cop-
per solubilized as an aqueous monoethanolamine or
ammoniacal complex. These copper systems include alka-
line copper quaternary (ACQ), copper azole (CA-B),
ammoniacal copper borate (ACB), ammoniacal copper
zinc arsenate (ACZA), and copper xyligen (CX-A) (Lebow
et al. 2004). Other aqueous systems include acid copper
Table 3. - AWPA E19 fixation test results.
Copper (mg/L) in Leachate
Days from Treatment to Sampling
1 3 7
15
4 k m3
Micro CQ 4 °C
2.2
1.8
1.7
1
ACQ-D 4 °C
10.7
10.3
8
6.4
Micro CQ 22 °C
1.9
1.5
1.2
0.9
ACQ-D 22 °C
9.2
6.6
3.9
2.4
Micro CQ ACQ-D 50 C oC I 3.2 I 2.8 4.1 5.2
6.4 kg/ m3
Micro CQ 4 °C
ACQ-D 4 °C
Micro CQ 22 °C
ACQ-D 22 °C
Micro CQ 50 °C
ACQ-D 50 °C
9.6 kg/mI
Micro CQ 4 °C
ACQ-D 4 °C
Micro CQ 22 °C
ACQ-D 22 °C
Micro CQ 50 °C
ACQ-D 50 °C
4.4
23.7
2.8
19.8
1.9
10.3
8.4
48.7
4.3
44.3
2.4
29.9
2.7
21.5
2.1
16.8
1.4
5.4
3.7
47.8
2.5
41.9
2.2
18.6
2.3
22.7
2.3
14.2
1.7
7
3.5
44.2
2.7
32.3
2.1
11.7
2.7
18.1
1.9
5.2
2
8.2
3.5
46.4
2.7
23.9
2.6
18.2
chromate (ACC) and water -borne copper naphthenate. As
well, there are copper systems used in Europe such as
copper betaine, but these systems are not widely used in
North America and won't be included here. The copper -
based formulations may be grouped as:
• Water -borne soluble copper formulations
• Oil -borne copper complexes
♦ Water -borne micronized copper formulations
Water -borne soluble copper formulations
CCA -
For most of the latter half of the 20th century, the
wood preservation industry was dominated by CCA. Since
the voluntary restrictions in 2004 though, its use has been
limited to industrial applications in structurally critical
members such as poles, piling, foundations, support
columns and the like. In the CCA-C formulation, chromium,
copper and arsenic are present at 47.5, 18.5, and 34 per-
cent, respectively, expressed as oxides. Copper provides
protection against fungi, chromium fixes copper and
arsenic in the wood, and arsenic provides supplemental
protection against copper -tolerant fungi and insects. CCA
was very much of a one -size -fits -all type of treatment
(Lebow et al. 2004).
Percent Loss of Micro CQ Compared to ACQ
Days from Treatment to Sampling
1 3 7 15 Average
21% 17% I 21% 16% 16% I 19%
21% 23% 31%
53% 39% 32%
19%
13%
10%
14%
13%
16%
18%
26%
24%
17% 8% 8%
10% 6% 8%
8% 12% 1 18%
38% 28%
29% 38%
11% 14%
37% 20%
24%
23%
8%
10%
11%
9%
14%
13%
FOREST PRODUCTS JOURNAL VOL. 58, No. 1 1 9

Table 4. - MSU soil block test results.
Test -
Institution Formula Condition, Brown -rot fungi White -rot fungi
Thresholds, kg/m$ Thresholds, kg/ms
G. P. N. T.
trabeum placenta lepideus lilacino gilua T. oersicolor L lacteus
1-MSU-E10 Micro L 1.6-1.8 2.2-2.6 <0.80 >3.2 1.4-1.6 <0.80
CA-1 NL 1.6-1.8 2.4-2.8 <0.80 >3.2 1.4-1.6 <0.80
1-MSU-E10 I Micro L
CA-2 NL
1-MSU-E10 I CA-B L
NL
2.1-2.2
2.2-2.6
1.6-1.8 2.1-2.4 <0.80
1.6-1.8 <0.80 <0.80
2-MSU-E10
Micro
L
3.5-4.2
8.3-8.6
<2.4
CQ
NL
3.7-4.0
8.3-8.6
<2.4
2-MSU-E10
ACQ-D
L
4.2-4.5
7.0-7.4
<2.4
NL
4.2-4.5
<2.4
<2.4
3-MSU-E22
Micro CAI
NL
0.60
2.6
<0.16
3-MSU-E22
CA-B
NL
<1.3
<3.2
3-MSU-E22
Micro CQ
NL
1.6
3.0
3-MSU-E22
ACQ-D
NL
1.8
<2.9
4-MSU-E22
Micro CA
NL
<0.80
1.6-2.4
5-MSU-E22
ACQ-D
1.2 -2.4
1.2 -2.4
aL = leached and NL = not leached
Today CCA-treated wood is often used as the refer-
ence standard in evaluating biological performance of new
preservatives. It has been difficult to develop low toxicity,
inexpensive replacements that can protect wood in such a
broad range of applications as CCA does. Now there are
more types of preservatives, and each is more closely tar-
geted toward specific applications. In addition, there is
greater emphasis on using the minimum retentions need-
ed depending on end -use application because the replace-
ments are more expensive. Leaching studies such as those
reported here indicate that these CCA alternatives release
preservative components into the environment at a rate
greater than or equal to that of CCA. However these com-
ponents have lower mammalian toxicity, and they are less
likely to cause concern in residential applications. CCA is
less corrosive to brass and steel than the other copper for-
mulations (Zhang and Jiang 2006).
ACQ -
Variations of ACQ include Types A, B, C, and D (AWPA
2008), which differ in the ratio of CuO to quaternary com-
pound, the particular type of quaternary compound used,
and the solvent system used. Types A, B, and D use dide-
cyldimethylammoniumchloride (DDAC) or didecyl-
dimethylammoniumcarbonate (DDA-Carb) as the co -bio-
cides. ACQ-B is an ammoniacal formulation, and ACQ-A
1.4
0.24
0.19
<0.80
<1.2
>3.2
>3.2
4.5-4.8
6.1-6.4
<2.4
<2.4
1.8
>4.5
1.6-1.8
1.6-1.8
4.5-4.8
6.1-6.4
<2.4
<2.4
1.4
>2.0
0.80
0.88
<0.80
<1.2
<0.80
<0.80
<2.4
<2.4
<2.4
<2.4
<0.16
0.64
0.72
0.80
<0.80
<1.2
and D are copper amine formulations. ACQ-C uses alkyl-
benzyldimethylammoniumchloride (ADBAC) as the co -bio-
cide and can be either an ammoniacal or an amine formu-
lation or use a mixture of the two solvents. ACQ-A has a 1:1
ratio of CuO to quaternary while the remaining three have
2:1 ratios. ACQ-B-treated wood has a dark greenish -brown
color and may have a slight ammonia odor until the wood
dries. Wood treated with ACQ-A or D has a light brown
color and little noticeable odor, while wood treated with
ACQ-C varies in appearance between that of ACQ-B and
ACQ-D, depending on the formulation. The multiple formu-
lations allow some flexibility in achieving compatibility
with a specific wood species and application. The ammo-
niacal ACQ-B formulation is used in the western United
States because it allows better penetration in difficult to
treat western species while treating plants in the remain-
der of the country generally use amine systems (Lebow et
al. 2004). Ammonia may also be added to amine formula-
tions to improve penetration in western species.
Copper azole -
Copper azole is another preservative formulation that
relies primarily on amine copper and a co -biocide to fur-
ther protect wood from decay and insect attack. The first
copper azole formulation CBA-A, included boric acid but
the more recent CA-B contains just copper (96%) and tebu-
10 NOVEMBER 2008

Table 5. - Additional E10 soil block test results.
Test -
Institution
Formula
Condition,
Brown -rot fungi Thresholds, /m'
White -rot fungi Thresholds, /m3
G. trabeum P. placenta N. lepideus Pl.ostreatus T. oersicolor L lacteus
1-MTU E10
Micro
L
<0.83 1.5 <0.83 <0.83 <0.83 <0.83
CA
NL
<0.83 1.5 <0.83 <0.83 <0.83 <0.83
1-MTU-E10
ACQ-D
L
2.1 2.1 <1.2 <0.83 <0.83 <0.83
NL
2.1 <1.2 <1.2 <0.83 <0.83 <0.83
G. trabeum P. placenta C. puteana Pl.ostreatus L lacteus
2-FOR-E10
Micro
L
<0.83
0.83
0.83-1.7
<0.83
<0.83
2-FOR-E10
CA
Micro
L
<1.0
<1.0
5.5
<1.0
<1.0
CQ
al, = leached and NL = not leached
conazole (4%). Wood treated with either copper azole for-
mulation has a brownish -green color and little or no odor.
The formulations are listed in AWPA standards for treat-
ment of a wide range of softwood species. Although listed
as an amine formulation, copper azole may also be formu-
lated as an amine -ammonia formulation with the ammonia
included when the formulation is intended for refractory
species (Lebow et al. 2004).
This year, a third copper azole formulation, CA-C, was
proposed for AWPA listing. This formulation uses 2 per-
cent propiconazole and 2 percent tebuconazole as the co -
biocides, and this combination of azoles has been shown
to be synergistic (Buschaus and Valcke 1995).
Ammoniacal copper zinc arsenate -
Ammoniacal copper zinc arsenate (ACZA) was devel-
oped in the early 1980s as an improvement on ammoniacal
copper arsenate (ACA) which dates back to the 1930s.
Used primarily in western North America for treatment of
Douglas -fir, AZCA contains copper oxide (50%), zinc oxide
(25%), and arsenic pentoxide (25%). The color of the treat-
ed wood varies from olive to bluish -green. The wood may
have a slight ammonia odor until it is thoroughly dry. As
with other ammonia containing preservatives, ACZA pene-
trates difficult to treat species so treating plants using
ACZA are located in western states where lumber from
many of the native trees is difficult to treat with CCA
(Lebow et al. 2004). ACZA reacts strongly with wood cells,
and it has been well tested in both terrestrial and aquatic
conditions in temperate zones. ACZA provides excellent
protection, especially in marine exposures (Rhatigan et al.
2000, Zahora et al. 2000).
ACC -
ACC contains 32 percent copper oxide and 68 percent
chromium trioxide and has been used since the 1920s main-
ly for wood in cooling towers. The high chromium content
prevents corrosion associated with acidic copper preserva-
tives. The treated wood has a light greenish -brown color
and little odor. While ACC provides good above ground
service life, wood used in ground contact may suffer occa-
sional early failures due to copper tolerant fungi attack. ACC
has limited critical structural application uses in the AWPA
although some applications such as posts are listed. It may
be difficult to obtain adequate penetration in refractory
wood species because ACC must be used at relatively low
treating temperatures and rapid reactions of chromium in
the wood can hinder further penetration during longer pres-
sure periods (Lebow et al. 2004).
Copper Xyligen -
Copper Xyligen (CX-A), which is also known as cop-
per-HDO, is a water -borne wood preservative based on Cu-
HDO (bis-(N-cyclohexyl-diazeniumdioxy)-copper), copper
carbonate, and boric acid as active ingredients. This sys-
tem is largely used in Europe, and some treaters have
begun to use the product in the United States. Currently,
the AWPA lists only above ground uses for CX-A.
Copper borate -
Copper borate is an effective treatment for wood com-
posites where protection against mold, decay, and ter-
mites is required. Oriented strand board containing a 10
percent copper borate formulation showed superior
resistance to mold growth and also provided similar pro-
tection as that of zinc borate and boric oxide against fun-
gal decay and Formosan termite attack. Copper borate
showed a negative impact on physical properties when
certain phenolic resins were used, but further research
reduced this impact. With proper phenolic resin selection,
or the use of MDI resin, adequate physical properties can
be obtained (Smart and Wall 2006).
Oil -borne copper complexes
Organometallic compounds are formed by the reaction of
metal ions with an organic ligand. Copper containing
organometallics used in wood preservation are copper naph-
thenate (CuNap) and oxine copper. Advantages of
organometallics include: (i) a relatively low metal content (if)
fewer metal corrosion problems than systems formulated
with uncomplexed copper ions and (iii) the metal coordina-
tion sites that are not complexed with the ligand could bind to
the carboxylic or phenolic groups in wood to make the formu-
lation relatively leach -resistant (Schultz et al. 2003).
Copper naphthenate oil -borne -
CuNap is the reaction product of a copper salt and
naphthenic acids (Barnes, et al. 2001). Oil -borne CuNap
FOREST PRODUCTS JOURNAL VOL. 58, No. 1 1 1 1

Table 6. - Ensis AWPC soil block test results.
Threshold, kg/m3
Formula
C. olivacea
F. lilacino gilva
G. abietinum
S. lacrymans
P. tephropora
L. crassa
Test 1
Micro CQ
1.9-3.2
1.0-1.9
<1.0
1.9-3.2
<1.0
<1.0
ACQ-D
1.9-3.2
1.0-1.9
<1.0
1.9-3.2
<1.0
1.9-3.2
CCA-C
0.6-1.2
0.6-1.2
<0.60
1.2-2.0
<0.60
<0.60
Test 2
C. olivacea
F. lilacino-gilva
G. abietinum
P. placenta
P. tephropora
L. crassa
Micro CQ-1
<0.60
> 1.3
<0.60
1.0-1.3
<0.60
<0.60
Micro CQ-2
<0.60
> 1.3
<0.60
> 1.3
<0.60
-
CA-B
<0.60
> 1.3
<0.60
> 1.3
<0.60
0.60-1.0
CCA-C
<0.60
1.2-2.0
<0.60
>1.3
0.60-1.2
1.2-2.0
has been used for over 50 years in wood preservation, typ-
ically in utility poles, fence posts, and lumber. Oil -borne
CuNap gives equivalent performance to creosote or pen-
tachlorophenol (penta) at appropriate comparable reten-
tions. Grace et al. (1993) showed CuNap to be effective
against Coptotermes formosanus for pine treated to 0.04 pcf
(0.64 kg/mD (as Cu). It has excellent potential for use as a
crosstie (sleeper) preservative (Barnes et al 2001). CuNap
is known to control many decay fungi, molds, mildew, dry
rot, certain marine growths, termites, other wood inhabit-
ing insects, and bacteria. One of the principal reasons that
CuNap is gaining market acceptance and is being com-
pared to other oil -borne wood preservatives is its low
mammalian toxicity. Almost all former penta plants in
Missouri and the western states of Montana, Wyoming,
and Colorado have switched over to CuNap. CuNap is typ-
ically supplied as an 8 percent concentrate that is
dilutable with a wide variety of organic solvents.
Copper naphthenate water -borne -
Water -borne CuNap presents some advantages such
as low volatile organic compound emissions and relatively
low cost by using water as the carrier (Kamdem et al. 1996,
Freeman 2002). The active ingredient is dissolved in a solu-
tion of an alkanolamine and/or ammonia in water. Kamdem
et al. (1996) reported that water -borne CuNap with 2 kgm-3
copper retention was sufficient to protect red oak
(Quercus rubra) and red maple (Acer rubrum) against some
white rot and brown rot fungi. Freeman et al. (2004) report-
ed that, after 6 to 7 years of field trials in Michigan, Florida,
and Mississippi, water -borne CuNap treated southern pine
(Pinus sp) at 0.76 kgml copper retention provided compa-
rable performance to wood treated with ACQ-C at 8.4 kgm-3
actives, CCA at 5.6 kgml actives and oil -borne CuNap at
1.86 kgm-3 copper retentions.
Oxine copper -
Oxine copper is formed by the reaction of copper with
8-quinolinol. The AWPA formulation consists of 10 percent
copper-8-quinolinolate, 10 percent nickel-2-ethylhexa-
noate, and 80 percent inert ingredients. It has been used
for wood treatment since the 1950s (Myers 1989). Oil -
borne oxine copper does not accelerate corrosion of metal
fasteners relative to untreated wood (Lebow 2007). A
water soluble form of oxine copper can be made with
dodecylbenzene sulfonic acid, and this corrodes metals
(Morrell 2005, Groenier and Lebow 2006). The treated
wood is colorless to greenish -brown and has little or no
odor (Morrell 2005). In recent years oxine copper has
increasingly been used as an alternative to copper naph-
thenate in above ground uses. It does not present the char-
acteristic naphthenic acid odor, is odorless and resistant
to hydrolysis. Oxine copper can be dissolved in hydrocar-
bon solvents but provides longer protection when deliv-
ered in heavy oil (Lebow 2007). It is an excellent fungicide
that is effective at very low concentrations and is also
toxic to insects (Myers et al. 1989, Groenier and Lebow
2006). Its greatest advantage is high efficacy and low mam-
malian toxicity. It is the only EPA -registered wood preser-
vative permitted by the U.S. Food and Drug Administration
for treatment of wood used in direct contact with food.
The low water solubility and low vapor pressure con-
tribute to its stability in wood and provide the necessary
longevity. Its greatest disadvantage is the high cost
(Morrell, 2005).
Water -borne micronized copper formulations
In these formulations, small "micronized" particles of
copper compounds are dispersed in the carrier instead of
using dissolved copper. There are a number of patents and
patent applications that specifically cover the micronized
copper technology as it relates to wood preservatives, and
the following provides a general review of the literature.
For more details, see Leach and Zhang 2006, Richardson
and Hodge 2004, Richardson and Hodge 2006, Zhang and
Leach 2005, and other patent literature by these authors.
Micronized particles are produced by mechanical
grinding of water- or oil -insoluble copper compounds with
aid of dispersing/wetting agents in a carrier using a com-
mercial grinding mill or by chemical means resulting in 90
percent or more of the particles being less than 1000 nm
size. The commonly used carrier is water, and commonly
12 NOVEMBER 2008

Table 7. - MSU E23 soil bed test results for brown rot decay.
Formula
Test 1
Micro CA
CA-13
Controls
Test 2
Micro CA
CA-B
Micro CQ
ACQ-D
Controls
Retention, kg/m3
1.6
3.4
5.1
1.6
3.4
5.1
1.6
3.4
5.0
1.6
3.4
5.0
3.2
6.4
9.6
3.2
6.4
9.6
97.5
99
98.4
96.6
96.5
96.4
94.1
94.5
94.4
93.8
92.3
92.3
93.9
aThe 6 month results were deemed unreliable by the researchers.
107.2
104.7
107.4
104.9
103.4
101.9
70.5
used dispersing agents are polymeric dispersants, which
attach to the surface of particles and keep the particles
away from each other. Also, the presence of dispers-
ing/wetting agents improves particle size reduction during
milling and stabilizes the particles during storage and
treating. The size of these particles can range from 1 to
25000 nm, and the particulate character may affect pene-
tration of wood cell walls and reaction with wood's molec-
ular constituents. The degree of penetration and uniformi-
ty of distribution of particles into the wood cellular struc-
ture is inversely related to the prevalence of particles with
relatively large particle size. Larger particles are generally
easier to prepare, but particles with long axes greater than
25000 nm may clog tracheids and inhibit the uptake of
additional preservative. If the particle size of the
micronized preservative is less than the diameter of the
window pit (typically 10,000 nm) or membrane openings in
a bordered pit (typically 400 to 600 nm) openings, com-
plete penetration and a uniform distribution of micronized
preservative in wood is expected.
Using field emission scanning electron microscopy
coupled with x-ray microanalysis (EDAX), Matsunaga et al.
(2007) examined the microdistribution of copper in south-
ern pine treated with micronized copper wood preserva-
tive to determine if it differed from that of wood treated
with conventional water -borne copper preservatives.
Results revealed the presence of nano -sized copper and
iron particles (from grinding media) ranging from 10 to 700
nm in micronized treated wood that were abundantly pres-
ent in pit chambers and on tertiary wall layers adjacent to
the lumens of tracheids and ray parenchyma cells. Copper
and iron were mainly present as separate particles.
Average % Strength at Month
9 12 18 24
102.6
104.1
102.3
101.1
100.6
99
44.4
96.2
97.2
95.7
96.5
95.4
93.5
21.9
96.5
98.5
97.5
97.4
96.6
94.7
96.3
97.8
98
95.4
93.6
91.7
34.8
80.5
87
88.8
81
89.2
88.1
2.1
65.3
80.1
84.3
79.1
84.7
86.1
0
30
46.5
63.3
69.9
53.2
70.2
72.6
Copper was also found in wood cell walls where its con-
centration was slightly higher in the middle lamella than in
the secondary wall layer. In this respect the microdistribu-
tion of copper in wood treated with dispersed copper
resembles that observed in wood treated with convention-
al soluble copper -based wood preservatives but the
amounts of copper in the cell wall components differed
between the formulations. In further work, Matsunaga et
al. (2008) refined their experimental techniques and indi-
cate that they are working to compare the concentrations
of metals in cell walls of wood samples treated with con-
ventional and micronized formulations.
Stirling et al (2008) reported distributions similar to
those of Matsunaga based on Environmental Scanning
Electron Microscopy (ESEM) and Energy Dispersive X-Ray
Spectrometry (EDS) results. X-ray analysis indicated that
there was a small amount of Cu in the cell walls in both
micronized copper and soluble systems. The authors sug-
gest that copper -containing particles in the treated wood
slowly release mobile copper, which may further pene-
trate through the cell wall.
However, the numerous particulate deposits of cop-
per in voids within the wood have also been discussed.
Archer (2007) raised concern that soft rot attack may be a
problem for micronized formulations. White -rot organisms
are also inhibited more by cell -wall treatment than by cell -
lumen treatment and numerous studies have shown that
the ability to control soft -rot in hardwoods depends on the
levels of copper in the S2 layer of wood cell walls (Hale and
Eaton 1986, Ryan and Drysdale 1988). Cell wall treatment
also improves the effectiveness of a preservative system
in resisting depletion and hence, the good performance of
FOREST PRODUCTS JOURNAL VOL. 58, No. 1 1 13

many water -borne wood preservatives has been attrib-
uted, in part, to the fact that they are absorbed into the
cell wall and uniformly distributed in the microstructure of
wood (Arsenault 1973).
Any suitable copper source can be used to obtain
micronized particles but basic copper carbonate is most
commonly used. Micronized formulations are also not lim-
ited to water -borne compositions; it is believed that parti-
cles carried in organic carriers, such as oils, will effective-
ly penetrate wood as well. Non-biocidal components
added to enhance performance may include water repel-
lants, colorants, emulsifying agents, dispersants, stabiliz-
ers, solubulizing agents, UV inhibitors and wood dimen-
sional stabilizers. Insecticides can be mixed with
micronized metal formulations and preferred co -fungi-
cides are quats and triazoles. Micronized copper carbon-
ate compositions generally have a pH in the range of 7 to
9, but inclusion of acids in the compositions will give a
neutral or acidic pH.
Wood treated with micronized copper is only slightly
more corrosive than untreated lumber and less corrosive
than other water -borne copper formulations to metal fas-
teners. The treated wood is also lighter in color; hence
lighter -colored paints and stains can be used.
Micronized formulations are not listed in the AWPA
standards, which contain only the various soluble formu-
lations. There are many reasons for this including formula-
tion confidentiality, extent of testing, and sponsor prefer-
ences. Accordingly, Table 1 shows a summary of required
retentions for some copper containing formulations cur-
rently listed in AWPA Standards.
In contrast, the International Code Council Evaluation
Services (ICC-ES) issues Evaluation Services Reports
(ESR) that list preservatives at retentions that may be dif-
ferent from those in the AWPA. An important point though
is that a product with an ESR is deemed satisfactory for
building code regulated uses. Thus, the lower retentions of
the ICC-ES dominate commercial use and several
micronized products are listed (Table 2).
Fixation and leaching of copper in treated wood
The effectiveness of fixation -chemical reactions that
prevent leaching is dependent on treating factors, such as
Table & - MSU E23 soil bed test results for soft rot attack.
Average % Strength at Month
Formula
Retention,
kg/m3
3
6
12
Micro CA
1.6
97.4
78.2
60.5
3.4
98.3
81.9
77.8
5.0
97.6
83.4
77.5
CA-B
1.6
96.5
81.5
70.1
3.4
96.2
82.4
84
5.0
95.4
79.2
81.4
Micro CQ
3.2
96.4
77.2
66.9
6.4
96.4
84.1
81.5
9.6
95.7
85.7
88.6
ACQ-D
3.2
96.8
80
70.5
6.4
94
80.8
81.9
9.6
93.7
80.3
82.7
Controls
-
75.8
42.4
0
preservative formulation, preservative retention, and pro-
cessing techniques, as well as post -treatment conditioning
factors, such as temperature, humidity, and air flow. CCA
has been studied more extensively than the other preser-
vatives. The most rapid leaching occurs within the first
months of service and is greatest in products with high
retention levels and high proportions of exposed surface
area, especially end -grain. Leaching is also increased by
exposing the wood to high water flow, low pH, and water-
soluble organic acids. Site, wood species, and preservative
type play major roles in copper leaching from treated
wood. Waterlogged sites, and/or sites with low pH cause
greatest loss to all treatments irrespective of wood species
and preservative type. Organic acids (humic, lactic, mal-
onic and fulvic acids) known to be associated with forest
litter are important agents of depletion (Cooper et al
2001). Less efficient fixation reactions, perhaps caused by
higher extractive content of some wood species and poor
preservative distribution (macro- and micro-) may result
in more leaching (Wakeling 2006). Movement of leached
chromium and copper appears to be quite limited in soil,
because the metals are tightly bound to organic soil con-
stituents. Generally, the preservative components are
least mobile in organic soils, slightly more mobile in clay
soils, and most mobile in sandy soils. In aquatic applica-
tions, the leached preservative components form com-
plexes with the organic sediment fines, and accordingly
are either deposited or moved downstream with the sedi-
ments (Lebow 1996).
Both oil -borne wood preservatives oxine copper and
copper naphthenate resist leaching because they are rela-
tively insoluble in water. In CCA treatment, chromium is
used to improve the fixation in wood. The reduction of the
reactive and mobile Cr (VI) to Cr (II1) is crucial in the for-
mation of insoluble complexes in CCA-treated wood with
the formation of chromium arsenate and chromium
hydroxide, while the products formed between copper
and wood carboxylate is relatively more soluble (Pizzi
1982a, b). This formulation limits copper leaching while
providing continuous bio-availability of copper toward
wood destroying organisms. The reactions in the fixation
of CCA in wood involve a number of mechanisms. The final
fixation products are dominated by chromium (III) arsen-
ate, chromium (III) hydroxide, and copper (II)- wood car-
boxylate complexes. Carboxylate groups are generated in
large numbers in the reduction of chromium (VI) by pri-
mary alcohol groups in lignin and carbohydrate fractions,
or in the oxidative degradation of lignin (Bull 2001).
The microdistribution of copper in the cell walls of
wood treated with CCA or CCB or the newer preservatives
that are free of chromium or arsenic has been extensively
studied using scanning or transmission electron
microscopy in combination with x-ray microanalysis
(Dawson-Andoh and Kamdem 1998, Petri et al. 2000,
Matsunaga et al. 2007). These studies have shown that the
copper concentration is higher in the middle lamella and
cell corners than in the secondary wall. This is attributed
to higher affinity of ionic copper for lignin, which reaches
its highest concentration in the middle lamella, than for cel-
lulose (Lebow 1996), or the increased density of the middle
lamella compared to the secondary cell wall (Cao and
14 NOVEMBER 2008

Kamdem 2005, Matsunaga et al.
2007) or to cation exchange with
weak acid groups such as pectic and
other uronic acids present in the cell
walls (Cooper 1991). Hence within
wood, various functional groups are
preferential adsorption sites for
transition metal ions irrespective of
the carrier solvent (Petri et al. 2000).
The importance of chromium -
free preservatives is increasing.
Since the use of chromium in wood
preservatives is significantly limited
or even banned in several European
countries, in order to use copper as
a fungicide in the future, new tech-
niques to improve copper fixation
have been developed (Humar et al
2007). The replacement of CCA by
alkaline copper compounds has
heightened awareness of the poten-
tial impact of copper losses on
aquatic organisms. Reducing these
losses will be necessary to avoid
continued regulatory actions
against the use of preservatives in
these environments. While post
treatment processing and coatings
can reduce losses, neither is com-
pletely effective. Adding chemical
compounds to the alkaline system
to complex or otherwise reduce
copper losses, much in the same
way that chromium acts in CCA, has
been attempted.
Alternatively, copper leaching
could be reduced by incorporating
additives into the preservative for-
mulation that block or slow copper
migration. Additives should be
hydrophobic and have the ability to
react with the wood matrix, convey
groups that can easily bond with
copper, enable some of the sorbed
copper to be released under wet
conditions and then bind to copper
again once the moisture content
decreases (Roussel et al. 2000).
Additives that limit metal loss may
also permit the use of lower initial
preservative loadings to produce
equivalent protection.
A common fabric softener,
di(hydrogenated tallowalkyl) dimethyl
ammonium chloride (2HT), reduces
copper losses from ACQ and copper
azole and hence improves overall
biological performance (Mitsuhashi
et al. 2007). The potential mecha-
nism by which 2HT alters copper
losses from wood remains unclear,
Table 9. - No -choice E1 Formosan test results.
rest-
Formula
Retention,
Weight Loss, %
Rating
Mortality,
Institution
kg/m3
1-LSU
Micro CA-1
0.80
5.2
8.2
44
1.6
4.7
8.3
30
2.4
7.3
8.2
37
3.2
5.9
8.9
50
1-LSU
Micro CA-2
0.80
5.5
8.2
39
1.6
3.8
8.4
54
2.4
5.5
8.2
78
3.2
3.8
8.4
77
1-LSU
Micro CA-3
0.80
1.3
9
80
1.6
1.7
9
87
2.4
3.9
9.1
30
3.2
3.1
8.9
1 24
1-LSU
ACQ-D
1.2
3.3
8.5
53
2.4
3.1
8.7
53
4.0
5.1
8.5
50
6.4
5.6
8.3
58
1-LSU
UNT
-
27.4
2
6
34
2-LSU
Micro CA
0.80
10.4
7.6
1.6
5.0
8.5
68
2.2
4.4
8.5
66
3.5
2.5
9.0
83
48
2-LSU
CA-B
1.8
2.2
8.9
3.7
1.8
10
37
65
2-LSU
Micro CQ
1.9
4.8
7.6
4.3
2.2
9.1
90
5.9
1.3
9.0
78
6.4
1.7
8.6
72
2-LSU
ACQ-D
3.8
0.6
10
77
6.1
0.3
10
64
2-LSU
CCA-C
3.8
1.8
9.4
100
6.2
1.4
9.3
100
2-LSU
UNT
-
31.5
1.6
8
3-MSU
Micro CA-1
0.80
4.5
9
a
1.6
1.7
9
2.2
2.5
9
3.2
2.1
9
3-MSU
Micro CA-2
0.80
4.0
9
a
1.6
2.9
9
2.2
2.4
9
3.2
2.7
9
3-MSU
CA-B
0.80
2.6
9
a
1.6
2.1
9
2.2
2.5
9
3.2
1 2.0
9
3-MSU
Water Treat
-
21.9
3.2
a
3-MSU
UNT
-
21.4
4
a
a See text for mortality data
FOREST PRODUCTS JOURNAL VOL. 58, No. 1 1 15

Table 10.
- MSU choice E1 Formosan test results.
Reticulitermes flavipes
Coptotermes formosanus
Formula
Condition
Retention, kg/m3 Weight Loss, %
Rating
Retention, kg/m3
Weight Loss,%
Rating
Micro CQ
L
2.4
0.11
9.2
2.4
0
9
NL
2.2
1.46
9
2.3
0.37
9
L
4.2
0.24
9.4
4.2
0.12
9
NL
4.2
1.56
9.2
4.2
0.5
9
L
7.0
0.37
10
6.7
0
9.2
NL
6.6
1.43
9.6
6.7
0.86
9
Controls
Both
13-60
0-5.8
38-46
0-3.2
ACQ-D
L
2.5
0.63
9
2.6
0.35
9
NL
2.6
2.09
9.2
2.6
0.25
9.4
L
4.2
1.14
9
4.2
0
9
NL
4.3
1.51
9.8
4.0
0.58
9
L
6.7
1.13
9
6.8
0
9
NL
6.2
1.59
8
6.4
0.79
9
Controls
Both
17-56
0.8-5.6
3548
0.8-3.6
Water
L
37.92
1.4
32.23
1.6
Treat
37.24
2.4
11.74
4.6
Water
NL
32.46
1.6
19.11
4.6
Treat
19.7
3.8
23.65
2.4
aL = leached and NL = not leached
Table 11.
- MSU E7 19 mm Gainesville, Florida stake test results.
Rating at
12 Months
24 Months
36 Months
Formula
Retention, kg/m3
DCY
TER
DCY TER
DCY
TER
Micro CA
1.6
10
10
9.9 10
9.4
9.4
3.4
10
10
10 10
10
9.8
Micro CQ
4.2
10
10
8.3 9.9
7.0
8.5
6.7
10
10
9.9 10
9.7
9.9
ACQ-D
3.8
10
10
5.6 7.2
3.3
5.1
6.1
10
10
9.8 10
7.8
9.4
Table 12. - MSU E7 19 mm Mississippi stake test results.
Rating at
12 Months
24 Months
12 Months
24 Months
Formula Retention, kg/m3
Saucier,
Mississippi
Dorman, Mississippi
DCY
TER
DCY TER
DCY
TER
DCY TER
Micro CA 1.3
10
9.9
10 9.8
9.8
10
9.8 9.8
3.4
9.9
9.9
9.9 9.7
10
10
10 10
4.8
10
9.9
10 9.9
10
10
10 10
CA-B 1.3 10
9.9
10
9.9
10
9.9
9.2
9.8
3.4 10
10
10
9.9
9.9
10
9.8
10
4.3 10
10
10
10
9.8
10
9.9
10
Controls - 6.1
5.5
2.3
1.7
6.5
8.4
3.1
6.6
but it is possible that hydrophobic interactions may
enable 2HT sorption on cellulose. While improved water
repellency could slow wetting and drying cycles, thereby
reducing the overall losses, other water repellants have
not produced the reductions in copper losses noted with
this compound. These results suggest that 2HT may have
other, more subtle effects on copper mobility.
Ammonia is a very effective fixation agent but its use
is limited due to emission and odor concerns. As noted,
ammonia was replaced with amines, and the copper:amine
molar ratio significantly affects penetration, fixation, and
performance of the preservative (Zhang and Kamdem
2000). However, leaching of copper from copper/amine
preserved wood is still higher compared to wood impreg-
nated with copper/chromium formulations. The rates of
stabilization or fixation of copper in ACQ-treated wood
were compared for different post treatment conditioning
temperatures (22 °C and 50 °C), solution concentrations
16 NOVEMBER 2008

(0.4 to 2.3%) and wood species. Copper stabilized much
faster at lower ACQ retentions and when conditioned at
50 °C compared to high retentions and stabilization at
22 °C. Species effects were minor (Ung and Cooper 2005).
The type of amine used affects the stability, polarity
and solubility of the copper amine complex. Cupric ions
form complexes with ethanolamine through amino and
hydroxyl groups in aqueous solution due to formation of a
five -member ring complex. These processes are significant-
ly affected by pH of the impregnated wood. If the copper -
amine complexes exist in wood by physical interaction,
they will leach easily. For better fixation, the copper -amine
complexes interact with wood through chemical reactions
with lignin carboxylic and phenolic hydroxyl groups
(Zhang and Kamdem 2000, Ruddick et al. 2001). In a ligand
exchange reaction mechanism, copper-ethanolamine com-
plexes exchange ligands with wood and release one or two
amine molecules. In the second possible reaction mecha-
nism, non -charged species of copper-ethanolamine com-
plexes are transformed into charged species during
impregnation. The carboxyl and phenolic groups can react
with the charged species to form a stable wood-copper-
ethanolamine complex (Zhang and Kamdem 2000).
A study of the interaction of copper
ethanolamine and wood components using
Fourier transform infrared spectroscopy (FTIR) Table 13.
confirmed that Cu-EA interacts with carboxylic
groups, phenolic hydroxyl groups and ester
groups on lignin to form copper carboxylate
and phenolate complexes (Zhang and Kamdem
2000). After treatment with copper-
ethanolamine, stable copper-nitrogen-lignin
complexes can be formed through reaction
with guaiacyl units in lignin. The fixation reac-
tion of copper preservatives in wood was stud-
ied using the reaction between vanillin, a lignin
model compound, and copper to form
di(ethanolamine)-bis (vanillinato)dicopper(Il);
[Cu(vanillin) (ethanolamine)12 (Xie et al. 1995,
Zhang and Kamdem 2000). Fixation of copper-
ethanolamine based wood preservatives is not
as good as fixation of copper -chromium ones,
because ethanolamine causes lignin depoly-
significant effect on accelerating copper fixation. The fixa-
tion rate is much higher and the predicted time needed for
complete fixation is much shorter at higher temperatures
(50 to 70 °C). The percentage of copper leached decreased
linearly with the length of post treatment exposure (Cao
and Yu 2007). Boron addition reduced copper fixation in
wood impregnated with copper-ethanolamine compared to
wood impregnated with copper-ethanolamine alone, but the
boron improved performance against the copper tolerant
fungus A. vaillandi (Pohleven and Humar 2006).
Thomason and Pasek (1997) postulated that copper
and boron are selectively adsorbed via two distinct and sep-
arate pathways. Adsorbed copper reacted exclusively with
hemicellulose carboxyl groups while boron reacted at other
locations, presumably forming esters with lignin phenols.
This mechanism differs from the above proposals for a cop-
per:lignin complex. The authors suggest that this difference
may be due to the heterogeneous structure of wood limiting
the formation of copper:lignin complexes whereas these
complexes can form under modeling conditions.
In a test on efficacy of a combination of copper-
ethanolamine and boron solutions against copper tolerant
fungi, Pohleven and Humar (2006) and Humar et al. (2005)
- Second MTU E7 19 mm Hawaii stake test results*.
Rating at
Formula
Retention, kg/ml
12 Months
21 Months
33 Months
DCY
TER
DCY TER
DCY
TER
Micro CA
0.80
10
10
9.5 9.8
5.3
8.9
1.6
10
10
10 10
9.8
10
2.5
10
10
10 10
10
10
3.2
10
10
10 10
10
10
Micro CQ
2.4
10
10
9.8 10
8.3
9.9
4.0
10
10
9.9 10
9.9
10
6.4
10
10
9.95 10
9.9
10
9.6
10
10
10 10
10
10
ACQ-D
2.4
10
10
9.7 10
8.4
9.9
4.0
10
10
9.9 10
9.5
9.8
6.4
10
10
10 10
9.9
10
9.6
10
10
10 10
9.8
10
UNT
-
8
10
0.9 5.6
0
7
merizatlon, resulting In leachable complexes of * Stakes origin
copper-ethanolamine-lignin monomers. Lignin Table 14.
degradation is reflected in higher organic car-
bon content in leachates, mass losses after
leaching and changes in mechanical proper-
ties. There was good correlation between
organic carbon in leachates and copper leach-
ing. The main source of organic carbon was
wood components (Humar et al. 2007).
Copper amine based preservatives can
have higher copper losses due to leaching
compared to CCA. A study on the effect of
temperature, relative humidity, and duration
of post -treatments on accelerating copper fix-
ation in ACQ-D in Chinese fir wood blocks
revealed that relative humidity has little effect
on fixation rate although moisture is required
f t d T t h
or reac Ions o procee empera ure as a
ally installed at Hilo and moved to Oahu at year 1.
- Ensis Innisfail, Australia stake test results.
Rating at 17 Months
Formula
Retention, kg/m3
Eucalyptus Radiata
Micro CQ
3.0
9 9.9
4.0
8.8 9.9
5.0
9.4 10
6.6
9.4 10
ACQ
3.0
8.1 9.9
4.0
8.4 9.9
5.3
8.6 9.8
6.7
9.4 10
CCA
0.80
2 5.9
1.6
7.3 8.4
2.9
3.9 9.9
UNT
-
0 0
FOREST PRODUCTS JOURNAL VOL. 58, No. 1 1 17

found that copper fixation is significantly improved by
addition of carboxylic acids. The boron increases efficacy
against fungi but decreases copper fixation. Octanoic acid
improves copper fixation, and slightly decreases effective-
ness against copper tolerant fungi (Humar et al. 2005).
Thus there must be a balance between fixation and per-
formance of impregnated wood. In leached specimens,
resistance to the copper tolerant fungus A. vaillantii is sig-
nificantly deceased, probably due to loss of boron.
Tannins have low toxicity as wood preservatives, but they
can fix biocides because of their excellent chelating prop-
erties. Co -impregnation in a two-step treatment with
copper, zinc, and boron showed that good retention of
copper (II) ions is achieved by first impregnating wood
with commercial chestnut tannin. The treated wood meets
the European standard for protection against decay. No
protection against blue -staining fungi was obtained as
boron retention was not achieved (Scalbert et al 1998).
Micronized copper fixation mechanisms
In contrast to soluble copper -based wood preserva-
tive systems such as CCA, CA-B and ACQ, wherein the Cu"
ions are believed to chemically "fix" in wood after treat-
ment, the micronized copper preservative particles with
polymeric dispersant molecules attached to the particle
surface are carried into wood through vacuum/pressure
impregnation and physically deposited into the wood
structure. After treatment, the micronized particles are
believed to "fix" to wood through strong adhesion
between the polymeric dispersants and wood fiber by sim-
ilar mechanisms as occur in wood coating applications.
The adhesion would anchor the micronized copper parti-
Table 15. — MSU E18 ground proximity test results.
cles within the wood and prevent the particles from being
dislodged by the normal weathering conditions that the
treated wood may be subjected to in service. In addition,
there is a small portion of free Cu" present in wood after
treatment as confirmed by the AWPA Ell leaching study
(Stirling et al 2008) and SEM Studies (Matsunaga et al 2007,
Stirling et al 2008). It is possible that the minor amounts of
free Cu+2 ions associated with the micronized particle for-
mulations bind to various components of the wood by sim-
ilar mechanisms as other soluble copper preservatives
such as ion exchange (Cooper 1991). However, the majori-
ty of fixation in micronized systems is believed to be sim-
ple deposition as opposed to reaction.
The importance of this distinction can be seen in
Table 3 where the results of an AWPA E19 Fixation test are
presented. At every sampling, the losses from the
micronized copper system were significantly less than the
losses from the matched soluble system. Interestingly,
there was an inverse relationship between retention and
copper loss in that lowest retention samples showed that
the micronized formulation lost about 30 percent as much
copper as ACQ-D did while the highest retention samples
showed that the micronized formulation lost about 10 per-
cent as much copper as ACQ-D did. The middle retention
of the micronized system lost about 20 percent of the cop-
per that ACQ-D lost.
Micronized copper systems compared
to amine -based systems
This section compares data from amine—solubilized
copper based wood preservative systems with copper sys-
tems that have the copper -based portion of the system as
sub -micron particle size dispersions.
Both biological and non -biological
tests are discussed. As is typical with
wood preservative research there
Rating at
Formula
Retention,
Hilo,
Saucier,
Hilo, Saucier,
kg/m'
Hawaii
Miss.
Hawaii Miss.
Test 1
12 months
Micro CA
1.6
10
10
2.4
10
10
CA-B 0.80 10 10
1.6
10
10
2.4
10
10
Micro CQ 1.6 10 10
4.8
10
10
ACQ-D 1.6 10 10
4.0
10
10
4.8
10
10
UNT — 9.1 9.3
Test 2
15 months
27 months
Micro CA
0.80
10
10
10 10
1.6
10
10
10 10
2.4
10
10
10 10
CA-B
0.80
10
10
10 10
1.6
10
10
10 10
2.4
10
10
10 10
Controls
—
7
9.9
1.2 9.4
were a number of slight variations in
the formulations tested. Essentially all
of the variations dealt with the co -bio-
cides though, and therefore the
micronized formulations are grouped
without regard to these small
changes. Therefore, "Micro CQ" is
used to designate systems with qua-
ternary co -biocides while "Micro CA"
is used for systems with azole co -bio-
cides. In some cases, two or more cop-
per azole variations were included in
the same test so the different formula-
tions are designated with a numerical
suffix. Generally speaking, the co -bio-
cides within a test are of similar char-
acter. It should be recognized that a
"Micro CA or CQ" in one test may not
be exactly the same as a "Micro CA or
CT in another test but this is unim-
portant. The primary emphasis is to
compare the Micro and amine prod-
ucts in the same test. Lastly, the
amine-solubilized formulations are
designated simply as CA-B or ACQ-D.
18 NOVEMBER 2008

The testing discussed in this section, unless other-
wise noted, was conducted in ISO 17025 conforming labo-
ratories that have also received accreditation by the
International Accreditation System OAS) or an equivalent
certifying agency. The tests were performed by using con-
sensus -based, industry -ratified and adopted test methods
with no significant deviations from the standardized proto-
col, unless otherwise noted in that section. The tests are
well-known within the industry.
Biological efficacy tests
Laboratory tests
Soil Block Test Summaries
Mississippi State University researchers conducted
Soil Block tests comparing micronized and soluble formula-
tions using both AWPA E10 and E22 protocols and common
test fungi (fable 4). In these tests, southern pine (Pinus
spp.) was used for brown rot fungi and beech (Fagus spp.),
cottonwood (Populus spp.) or sweetgum (Liquidambar
styraciflua L.) for the white rot fungi. It should also be men-
tioned that all of the untreated controls in the soil block
tests discussed here showed good fungal virulence on the
untreated hardwood or softwood species used.
The thresholds determined in the first E10 test for two
micronized copper azole formulations and an amine based
copper azole were very similar in the leached condition.
Note that one micronized formulation was only tested
against the copper tolerant P. placenta. In all, there were
no meaningful differences determined for the various for-
mulations although the unleached CA-B control "apparent-
ly" had a lower threshold with P. placenta. Presumably,
this difference is due to soluble, unfixed components that
are readily leached.
A second MSU E10 test compared a micronized copper
quaternary with soluble ACQ. In this case, two brown rot
fungi, P. placenta and T. lilacino7gilva, had significantly higher
Table 17. - Michigan State El 1 leaching test results.
Table 16. - CSIRO lunchbox termite test results.
Wood Formula Retention,
kg/m3
Wt. loss ('9)
C. M.
acinaciformis darwiniensis
Pine
Micro CQ
3.2
0.3
5.8
6.2
0.2
1.4
ACQ-D
3.4
0.4
5.1
6.2
0.6
3.0
CCA-C
3.5
0.6
2.0
6.9
0.4
3.1
Water
-
91.7
94
Gum
Micro CQ
3.2
0.9
7.6
6.4
0.7
2.8
ACQ-D
2.9
1.5
9.1
6.2
1.9
3.1
CCA-C
3.2
0.7
2.3
5.6
1.0
2.5
Water
-
67.8
98.2
thresholds for the micronized formula compared to the sol-
uble one. This is somewhat anomalous in that a third MSU
Soil Block test that was done by the E22 procedure had the
micronized copper product with a similar threshold to the
soluble formulation for P. placenta. As reported later in Table
6, testing with the synonymous Fomitopsis lilacino-gilva
showed that the Micro CQ in that test gave the same thresh-
old as ACQ-D. Thus, the performance in the second MSU E10
test may be anomalous or an indication of sensitivity of the
quaternary portion of the formulation.
MSU researchers also conducted AWPA E22 Soil Block
tests using the same four brown rot fungi and two white
rot fungi. For the six fungi in the third MSU test, the
thresholds for the micronized formulations were the same
or better than the thresholds for the soluble products.
Other E22 tests run by MSU gave the results shown as Test
4 and Test 5. It should be noted that the
formulas listed were not tested at the
same time but the results show similar
th s h lds a1-1,1-1,1-1,
s
FOREST PRODUCTS JOURNAL VOL. 58, No. 1 1 19

Table 18. - MSU and TPI El 1 leaching test results.
Component loss (/)
Test-
Formula
Retention,
Copper
Quat
Chromium Arsenic
Institution
kg/m3
1-MSU
Micro CQ
4.0
7.3
7.7
- -
6.4
6.4
8.0
- -
1-MSU
ACQ-D
4.0
15.1
7.4
- -
6.4
19.3
6.4
- -
1-MSU
CCA-C
4.0
4.4
-
6.8 30.3
6.4
10.5
-
2.8 25.4
Copper
Quat Tebuconazole
2-TPI
Micro CA
1.9
1.5
-
1.5
3.2
1.4
-
3.3
2-TPI
ACQ-D
4.0
14.0
2.7
-
6.4
20.4
3.7
-
3-TPI
Micro CA
1.6
2.14
BDL
3.2
2.18
BDL
4.8
1.86
BDL
3-TPI
CA-B
1.6
5.42
27.59
3.2
6.29
20.33
4.8
9.74
18.32
Table 19. - MSU E20 soil leaching test results.
Component loss ('9)
Copper Quat
4 kg/m3 Retention
Micro CQ-SOIL 1
3.7
29.6
Micro CQ-SOIL 2
6.2
16.8
Micro CQ Average
5.0
23.2
ACQ-SOIL 1
15.8
29.8
ACQ-SOIL 2
23.4
15.1
ACQ Average
19.6
22.4
6.4 kg/m3 Retention
Micro CQ-SOIL 1
-4.1
22.3
Micro CQ-SOIL 2
9.3
19.2
Micro CQ Average
2.6
20.7
ACQ-SOIL 1
11.5
22.1
ACQ-SOIL 2
24.8
12.9
ACQ Average
18.2
17.5
Table 20. - TPI E20 soil leaching test results.
Component loss (`9)
Formula Retention, kg/m3 Copper Quat Tebuconazole
Micro CA 3.2 14.1 - 10.8
ACQ-D 6.4 26.6 7.3 -
this case, the Micro CQ did not perform as well
as the Micro CA.
Ensis (formerly CSIRO) used the
Australasian Wood Preservation Committee
(AWPC) protocol for soil block testing that is
functionally the same as the AWPA E10 test.
After 12 weeks of exposure, the mass losses
for leached blocks of radiata pine with brown
rot fungi or eucalypt with white rot fungi were
as shown in Table 6. In this case, the brown
rot fungi used were: Coniophora olivacea,
Fomitopsis lilacino gilua, Gleophyllum abiet-
inum and Serpula lacrymans. The white rot
fungi used were Perenniporia tephropora and
Lopharia crassa. The results show fungal con-
trol for micronized formulations at retentions
comparable to or lower than the soluble ACQ-
D and CA-B used in the test.
A second soil block test using AWPC proce-
dures was conducted by Ensis using lower reten-
tions. The copper tolerant Postia placenta was
used in lieu of S. lacrymans in this second test. In
both Ensis tests, the micronized products gener-
ally performed similar to or better than the solu-
ble copper azole or CCA C controls.
To summarize the above 8 soil block
tests, the performance of the micronized sys-
tems is essentially the same as the soluble
control formulations for a wide variety of
brown rot and white rot fungi. In one test, the
micronized formulations had a meaningful dif-
ference in the thresholds, but other tests con-
tradict that result.
Soil bed test summaries
The AWPA E23 Soil Bed test can be con-
trolled to favor brown rot (Basidiomycete sp.)
attack by keeping the soil moisture content in
the range of 40 to 80 percent. Two soil bed
tests were conducted favoring brown rot con-
ditions by Mississippi State University
researchers and the results are summarized
in Table 7. It should be noted that the average
percent strength loss is used to evaluate
decay attack in this test. The two brown rot
tests show similar performance for the two
micronized formulations in Table 7 with their
matched soluble counterparts.
Similarly, the AWPA E23 test can be con-
ducted where soft rot attack is favored by con-
trolling the soil moisture near saturation
(>90%). Table 8 presents the results of the MSU
E23 test under soft rot favoring conditions and
there does not appear to be any differences in
performance between the micronized and the
soluble products in this soft rot test. It should
be noted that the testing in Table 7 and 8 was
done at the same overall copper retention for
both the azole and quaternary products.
Scion (formerly New Zealand Forest
Research Institute) is currently conducting a
20 NOVEMBER 2008

Table 21. - TPI E12 coupon corrosion test results.
soft rot test. The AWPC protocol is
being used with stock soil taken from
the Scion forest nursery. The soil
was wetted to more than 100
percent water holding capacity before
stake installation and high soil mois-
ture was maintained during exposure.
Soil temperature was maintained at
79 °F (26 °C). There is no significant
difference in the micronized and solu-
ble products at comparable retentions
in this soft rot test after 22 months
(Fig. 1).
The results of the MSU and the
Scion accelerated laboratory tests show
that the soluble and micronized formu-
lations have similar performance
against soft rot fungi.
Termite test summaries
AWPA E1 No Choice testing with
Formosan Subterranean Termites (FST,
Coptotermes formosanus) was done at
Louisiana State University (LSU) and
Mississippi State University with
micronized formulations with the
results shown in Table 9. As explained
above, the co -biocide portions of the
micronized formulations are slightly dif-
ferent and therefore designated by a
numerical suffix. Also, note that consid-
Coupon Type
Formula
Retention, kg/m'
Corrosion (mpy)
C1010 Steel
Micro CA
1.1
2.3
8.0
3.2
14.0
CA-B
1.2
4.2
2.6
8.3
3.7
10.5
Water only
0.2
Hot Dipped
Micro CA
1.1
0.9
Galvanized
2.3
1.3
3.2
3.5
CA-B
1.2
2.0
2.6
3.3
3.7
2.2
Water only
-0.1
CDA 110 Copper
Micro CA
1.1
0.1
2.3
0.1
3.2
0.1
CA-B
1.2
0.2
2.6
0.3
3.7
0.3
Water only
0.1
2024 Aluminum
Micro CA
1.1
0.7
2.3
2.2
3.2
6.6
CA-B
1.2
-0.1
2.6
0.1
3.7
0.1
Water only
-0.1
Table 22. - E12 coupon corrosion test results.
Corrosion (mpy)
Test -Institution
Formula
Retention, k /m3
Steel
HDG
Alum.
Brass
Copper
SS
1-TPI
Micro CA
1.9
2.56
1.10
0.19
0.07
3.7
2.06
2.14
-0.27
0.06
ACQ-D
4.5
8.67
-0.17
0.33
0.15
7.0
13.74
0.80
0.23
0.24
Untreated
-
-0.07
-0.66
0.38
0.03
2-SUNY
Micro CA-1
3.4
1.7
1.9
0.1
0
0
0
Micro CA-2
3.4
2.6
2.7
0.1
0
0
0.1
CA-B
3.4
7.1
3.0
0
0
-0.2
0
Micro CQ
6.4
1.6
1.6
0
-0.1
-0.1
0
ACQ-D
6.4
7.7
3.2
0.1
0
-0.2
0
CCA-C
6.4
1.6
2.1
0.1
0
-0.1
0
Untreated
-
0.3
0.5
0
-0.1
-0.1
0
3-SUNY
Micro CQ-1
4.0
2.8
0.9
0.3
0.1
6.4
2.7
0.8
0.5
0.1
Micro CQ-2
4.0
3.5
1.0
0.4
0.1
6.4
4.4
1.1
0.4
0.1
ACQ-D
4.0
12.1
1.1
0.4
0.1
6.4
15.7
1.4
0.3
0.3
CCA-C
4.0
3.0
0.8
0.2
0.1
6.4
3.7
1.0
0.3
0.1
UNT
1.7
0.4
0.1
0.1
FOREST PRODUCTS JOURNAL VOL. 58, No. 1 1 21

Table 23. - Michigan State ISANTA fastener corrosion test results.
Retention,
kg/m3
Coated
Screw
Dry Wall
Screw
Sheet Metal
Screw
Average weight loss (%)
HDG Common
Nail Nall
Aluminum
Nall
Copper
Nail
Micro CA-1
3.4
0.51
0.33
0.01
1.59
2.85
0
0.01
Micro CA-2
3.3
0.56
0.33
0.01
1.79
3.4
0.02
0
CA-13
3.3
1.29
0.38
0
2.82
5.2
0
0.01
Micro CQ
6.2
0.58
0.34
0
1.71
2.52
0.02
0
ACQ-D
6.2
1.38
0.4
0
3.35
6.28
0
0
CCA-C
6.4
0.69
0.37
0.01
1.64
2.23
0.01
0.01
UNT
0.65
0.37
0
1.51
1.41
0.01
0
Table 24. - ASTM D-143 bending strength test results.
Test
Institution
Formula
MORI
MOEb
WML°
Test 1
MSU
Micro CQ (3.4 kg/m3)
0.99
0.97
1.09
Micro CA-1 (3.4 kg/m3)
0.99
0.97
1.04
Micro CA-2 (3.4 kg/m3)
1.03
0.98
0.95
UNT
1
1
1
Test 2
SUNY-ESF
Micro CQ (6.1 kg/m3)
0.97
1.00
0.85
ACQ (5.9 kg/m3)
1.03
1.06
0.69
UNT
1
1
1
Test 3
TPI
Micro CA (5.4 kg/m3)
1.00
1.04
0.90
CA-B (5.3 kg/m3)
0.98
1.01
1.04
Water
1
1
1
a Modulus of Rupture b Modulus of Elasticity c Work to Maximum Load
erably lower retentions of some of the micronized formu-
lations are tested in comparison to their respective solu-
ble controls.
In the first LSU test, the results were consistent for the
3 micronized copper azole formulations since tebucona-
zole does not have insecticidal properties and the copper
content was the same in each formulation. There was
slight weight loss in both the experimental and ACQ-D
(control) treatments but this is due to "nibbling" by these
voracious termites.
Another No Choice E1 Formosan test at LSU compared
two micronized formulations, Micro CA and Micro CQ, with
ACQ-D , CAB, CCA C and untreated wood. In this test, at sim-
ilar copper retentions, the performance of the micronized
formulations was similar to that of the soluble systems.
Mississippi State University (MSU) also performed
AWPA E 1 Formosan testing using the No Choice procedure.
Essentially 100 percent termite mortality was obtained
with all treatments and the two controls had <33 percent
termite mortality. The micronized and the soluble treat-
ment had similar weight losses and ratings in this test.
In a second E1 test conducted at MSU, the Choice pro-
cedures were followed and both Formosan and the com-
mon subterranean termite (Reticulitermes flavipes) were
used. The samples were also tested in the leached and
non -leached condition. The results comparing Micro CQ
and ACQ-D are in Table 10. Again the various treatments
had 100 percent termite mortality while the controls were
<33 percent, and again the performances of both the
micronized and the soluble formulations were similar.
As shown by the above four tests, there is no meaning-
ful difference in the performance of micronized formula-
tions compared to their soluble counterparts or to other
waterborne formulations for either common subterranean
or Formosan termites. This is as expected since copper is
the dominant termiticide in the formulations and it is pres-
ent in equal amounts whether or not the formulation is
micronized.
Field efficacy tests
For most wood preservation researchers, the most
important criteria for judging performance of a system is
the comparative performance of that system against well-
known standardized preservative systems in field efficacy
tests. For many decades, the key indicator of long-term
performance has been the relative ranking of the various
retentions of the formulation compared to similar reten-
tions of CCA-C. More recently, CA-B or ACQ-D have been
the primary comparators but it should be kept in mind
that these formulations were standardized based on their
relative performance to CCA-C.
For this paper, the primary focus is on the relative
performance of the micronized formulations compared to
the soluble versions of the same formulation. There is no
reason to believe that this relative performance between
the micronized and the soluble systems will not continue
22 NOVEMBER 2008

for longer periods of time. This provides a mechanism to
gauge properties for micronized formulations for dura-
tions longer than the tests themselves.
Field stake test summaries
The AWPA E7 Field Stake test method allows a variety
of stake sizes which range from the relatively small
Fahlstrom size (4 by 38 by 254 mm) up to the IUFRO size of
25 by 50 by 500 mm. The cross-section of the IUFRO stake
is more than 8 times that of the Fahlstrom stake so the
fastest approach to determine decay and termite attack is
to use the small Fahlstrom stakes. The large surface to vol-
ume ratio provides an acceleration factor so performance
can be determined in shorter exposure periods.
Figure 2 shows a comparison of Micro CA, Micro CQ
and ACQ-D at four different retention groups using
Fahlstrom stakes in an AWPA E7 test in Gainesville, Florida.
After 3 years of exposure, the highest retentions of the
three formulations are rated at 8 or 9 while the next high-
est retentions are all grouped near a 6 rating. The third
retention group is rated from 1 to 4 while the lowest reten-
tion group is at 1 or less. Importantly, the performance of
the two micronized formulations matches that of the solu-
ble formulation throughout the various retention groups.
It should be noted that the last rating of all of the stakes
was independently done by MSU personnel to avoid any
bias.
A longer term AWPA E7 test with Fahlstrom stakes is
shown in Figure 3. After 5 years of exposure in Gainesville,
the Micro CQ at 6.4 kg/m3 retention is clearly outperform-
ing the ACQ-D at 6.7 kg/m3 retention. The performance of
the two systems in the two lower retention groups is the
same though. Again the last inspection of these stakes was
performed by MSU personnel.
An AWPA E7 test with 19 by 19 by 450 mm stakes is
underway at Gainesville. The last inspection of these
stakes was also performed by MSU personnel and the
results are summarized in Table 11. The higher retention
approximates the ground contact retention for each for-
mulation while the lower retention is approximately the
above ground retention. It is apparent that Micro CA and
Micro CQ in this test are outperforming ACQ-D at both
retention levels.
A second 19 mm stake test is currently being conduct-
ed by MSU at two sites in Mississippi and 2 year data are
presented in Table 12. There is little differentiation
between the formulas in this test and more exposure time
will be needed for the treated specimens. The untreated
controls are completely destroyed so there is good activi-
ty at these sites.
Figure 4 shows test results with 19 mm stakes being
conducted in Hilo, Hawaii, by Michigan Technological
University. In this case, the comparator is a proprietary
organic biocide system that was tested at comparable
retention levels as the Micro CQ. Obviously, the Micro CQ
is performing much better than the organic system. Soft
rot cavities and narrow bore holes were found in the
organic biocide stakes as well as the untreated stakes in
this test (Stirling et al. 2007). This further demonstrates
the soft rot resistance of the micronized formulations in
test at this site.
Figure 1. SCION Soft Rot Test Results
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EXPOSURE [months]
—5.GMlero Cq --6.6 ACQZ
—5.0 Micro Co -5.0AC43-0
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Figure 2. AWPA E7 Test with Fahlstrom
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A second MTU test in Hilo with 19 mm stakes has the
results shown in Table 13. In this test, the lowest retention
of Micro CA has about half the copper of the lowest reten-
tions of the quaternary formulations so it is not surprising
that these stakes are beginning to show some attack.
There is considerable activity at the site since the untreat-
ed controls have failed completely.
A field stake test using Australasian Wood
Preservation Committee (AWPC) procedures is being con-
ducted by Ensis in Innisfail, Australia using 20 mm stakes.
The 17-month ratings are available and these have been
adjusted to the 10 scale familiar to North America
researchers (Table 14). The micronized formulation has
ratings that are somewhat better than the soluble formula-
tion for the hardwood (Eucalypt) samples while there is
FOREST PRODUCTS JOURNAL VOL. 58, No. 1 1 23

Figure 3_ Second AWPA E7 Test with
Fahlstrom size Stake
10 —
t
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W •
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1
0 io 20 w 40 U so
EXPOSURE (9wn1hsi
—BA Micry OO �3.2 Mk rn CO �1,8MIcrn CQ
--s.7Aco-o-4.2nco-o-1.1FncQ-o
----UNr
Figured. Hilo HI Test Results
a 41*
1
LU
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1
0
0 10 20 30 40 5C
EXPOSURE jrnonths)
—9 8.1 MIsra OQ --Organic Rxin1
�UWmCQ -Organic Ratn2
�Z,DMIcrnca-Qrganie Ratn3
�15Mlcry CQ y—OrganicRW4
basically no attack on the softwood samples. The site is
very aggressive as shown by the attack on the CCA treat-
ed Eucalypt and both the micronized and the amine formu-
lations are performing better than the CCA treated hard-
wood. This suggests that soft rot control with the alternate
formulations is better than the control with CCA. Soft rot
control in hardwoods has been a long known problem with
CCA (Hulme and Butcher 1977).
Overall, the 7 field stake tests show good efficacy of the
micronized formulations. In every case, the performance of
the micronized system was similar to or better than its solu-
ble counterpart at equivalent retentions. The tests are being
conducted in well-known, high hazard sites in Australia,
Florida, Hawaii and Mississippi. There is no reason to believe
that the long-term performance of micronized systems will
not match that of other waterborne systems.
Ground proximity test summaries
Two AWPA E18 ground proximity tests are underway
in Hilo, Hawaii, and Saucier, Mississippi, under the aus-
pices of MSU personnel. The first has only 12 months of
exposure (Table 15) and has limited decay. The second
has 27 months duration, and the Hawaii untreated controls
are severely decayed. However, the two ground proximity
tests need more exposure time to provide more discrimi-
natory results.
Field termite test summary
A field termite test was conducted by CSIRO person-
nel according to AWPC procedures. Blocks of either radia-
ta pine (Pinus radiata) or spotted gum (Corymbia macuia-
ta) were treated with formulations, leached and then
exposed to either Coptotermes acinaciformis or
Mastotermes darwiniensis termites. The latter termite is a
voracious feeder while the former is similar in aggressive-
ness to the Formosan subterranean termite found in the
United States. For this test, the treated blocks were placed
in metal "lunch box" containers that were attached by
plastic pipe to termite infested trees. The test exposure
continued until the untreated controls were destroyed,
which was 12 months for the C. acinaciformes and 5
months for the M. darwiniensis (Table 16). The micronized
formulation performed similarly to ACQ-D in this field test
with these two termite species.
Laboratory property tests
Water leaching test summaries
AWPA El 1 Leaching tests were conducted by Michigan
State University (Table 17), Mississippi State University
(Table 18) and twice by Timber Products (Table 18). The
results of these tests show that the micronized systems
lose considerably less copper than the amine-solubilized
systems when evaluated in this aggressive leaching
regime. In the first two tests, the micronized systems had
about half of the copper losses as the soluble systems
while in the third test, the losses of copper from the
micronized system were only a tenth of the soluble sys-
tem. Generally, the co -biocide losses are approximately
the same — which is to be expected —except in the second
TPI test where the tebuconazole losses were below the
detection limit.
Laboratory soil leaching test summaries
Mississippi State University researchers conducted
AWPA E20 Soil Leaching using two different soils (Table
19). One was obtained from the Saucier field test site
while the other was purchased from a local agricultural
cooperative. Surprisingly, the two soils had similar
chemical and physical properties considering the con-
siderably different sources. However the copper losses
were generally higher in the agricultural soil. Overall
though, the average copper losses from the micronized
system were about one-fourth of the copper losses from
the soluble system.
24 NOVEMBER 2008

The second AWPA E20 test was done by Timber Products
(Table 20), and the copper losses from the micronized formu-
lation were about half those of the soluble system.
Results of the two soil leaching tests show that the
micronized systems lose considerably less copper than
the amine-solubilized systems. This is in agreement with
the water leaching tests discussed above.
Effects on treated wood properties
Treated wood -metal coupon
corrosion test results
All of the following AWPA E12 coupon corrosion test-
ing was conducted with 10 replicates of each condition.
This is a significant improvement over the 3 replicates
used in the test standard since the test variability is con-
siderably less with more replicates.
E12 coupon corrosion testing has been conducted by
Timber Products Inspection on a number of micronized
formulations. The results from one study are in Table 21
where the micronized and amine treating solutions were
chosen to cover the range of above ground and ground
contact retentions for the formulation. Generally the rates
for the Micro CA were similar to the rates for the soluble
treatment except for aluminum. There the micronized ver-
sion appeared to be more corrosive which is somewhat
surprising in light of other tests.
Corrosion rates for additional E12 coupon corrosion
tests conducted by TPI and the State University of New
York —Environmental Science and Forestry (SUNY) are
shown in Table 22. In the TPI test, the rates for the
micronized formulation were similar to the soluble formu-
lation for aluminum, brass and hot dipped galvanized and
considerably lower for the mild steel.
SUNY-ESF researchers determined that the
micronized formulations appeared to have lower or simi-
lar corrosion depending on the metal in one test. In a sec-
ond corrosion test, SUNY-ESF determined the micronized
formulations again show good corrosive properties rela-
tive to the other water-bornes. In this test, the corrosion
rates for the micronized formulations were about one-
third those of the soluble counterparts for mild steel.
These four tests show that, within the experimental
variation, the corrosion rates determined for the
micronized formulations were the same or better than
those for the soluble formulations. In one case, it appeared
that the micronized rate was high with aluminum but the
other three tests showed that the micronized formulas
perform well with this metal.
The protocol developed by the AWPA in cooperation
with the International Staple, Nail and Tool Association
(ISANTA) was used by Michigan State University
researchers to evaluate fastener corrosion in contact with
micronized formulations. The results in Table 23 demon-
strate that the micronized formulations had less corrosion
with the seven screws and nails tested. In most cases, the
micronized formulations had weight losses similar to or
less than those for CCA-C.
ASTM D-143 bending strength tests results
A number of bending strength tests have been performed
following ASTM D-143 procedures. Within a test series, the
results can be compared to either the untreated or water -
treated control. The results for 3 such tests are presented
in Table 24 and show that the micronized formulations do
not impact strength properties to any significant degree. In
fact, the micronized strength properties are usually within
a few percent of those of the water treated or the untreat-
ed controls.
Other test results
Two recent publications discussed copper -containing
preservatives and presented results of nonstandard pro-
cedures (Goodell et al. 2007, Preston et al. 2008). At first
glance, one would reach the conclusion that the first pub-
lication demonstrated that none of the commercially
available (and soluble) copper preservatives are very
effective while the second showed that the micronized
formulations are even less effective than the soluble ones.
Since these two conclusions run counter to the volumi-
nous testing on the soluble and the micronized formula-
tions, it appears reasonable to question the conclusions.
It seems more likely that the results reported in these two
papers are due to the nonstandard test procedures used
where test samples were cut from larger pieces and little
to no data were given on co -biocide analysis of the test
specimens. The results of these nonstandardized tests are
consistent with attack by copper tolerant fungi on inter-
nal parts of treated products rendered vulnerable by
stripping of co -biocides and exposed to attack by cutting
out test samples.
Summary and conclusions
The results of the laboratory and field tests summa-
rized above show that micronized formulations perform as
well or better than their amine-solubilized counterparts.
The laboratory biological efficacy tests for fungal decay,
soft rot attack and termite resistance demonstrate similar
thresholds or performance levels across the board. The
field efficacy tests show good performance of the
micronized systems at appropriate retentions for both
above ground and ground contact applications. Property
testing demonstrated that micronized systems leach less
than the soluble counterparts and have improved corro-
sion properties. No deleterious effects were noted on
strength properties.
The variety of copper -based wood preservatives
has increased in recent years since copper exhibits
good biocidal activity. However, any formulation of cop-
per -based wood preservatives must be efficacious
against copper -tolerant fungi. Several co -biocides are
used to enhance efficacy against copper tolerant fungi.
Copper remains the primary biocide component used to
protect wood used in ground contact or fully exposed to
the weather.
Copper can be fixed in wood through complexing, lig-
and exchange, chelating, and precipitation with wood
components. Copper toxicity is associated with free
cupric ion in a biological system and copper interferes
with the metabolism of wood decay fungi.
FOREST PRODUCTS JOURNAL VOL. 58, No. 1 1 25

Most copper -based products have found good
growth markets in Europe and Japan, but only Copper
Quarternaries and copper azole have seen large commer-
cial success in the United States. Considerable research
continues with copper -based preservatives, and the
recent introduction of numerous micronized versions is
an offshoot of that research. Extending the growth of cop-
per -based preservatives into the future will depend on
continued research improvements.
Authors' Notes
This paper contains proprietary data that is the prop-
erty of the owners of the original studies. The technology
that is the subject of this paper is or may be subject to
claims for protection under various U.S. and foreign
patents and patent applications. By providing information
to the authors for use in the preparation of this paper none
of the parties providing such information in any way waive
their rights pursuant to such patents and patent applica-
tions or intend in any manner to grant any license or per-
mission, express or implied, to any other party (including
without limitation the other parties providing information
to the authors for use in the preparation of this paper) to
use the technology.
The authors believe that in good faith no data or find-
ings have been withheld from them in preparing this
review and base their conclusions on data furnished to
them under secrecy agreements and under waiver of non-
disclosure terms.
About the authors
Mike H. Freeman is an independent wood scientist in
Memphis, Tennessee; ([e-mail]). Craig R.
McIntyre is principal of McIntyre Associates, Inc. in Walls,
Mississippi ([e-mail]).
The authors dedicate this article in loving memory
of Mrs. Craig (Marie) McIntyre.
Precautions
This publication reports research and data involving
pesticides. It does not contain recommendations for their
specific or individual use, outside of the registered pesti-
cide U.S. EPA label, nor does it imply that the uses dis-
cussed here have been registered. Appropriate State
and/or Federal agencies must register all uses of pesti-
cides before they can be recommended. Some pesticides
discussed in this article are restricted use pesticides
(RUP's) and can only be purchased and used by a certified
pesticide applicator.
Pesticides can be injurious to humans, domestic ani-
mals, desirable plants, and fish or other wildlife if they are
not handled or applied properly. Use all pesticides selec-
tively and carefully. Follow recommended practices for the
disposal of surplus pesticides and pesticide containers.
Always read and follow U.S. EPA approved labeling and use
the product only for its intended use and at the approved
use rate. Remember, the label is the law; Material Safety
Data Sheets are for guidance only.
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