|
TO WHOM
IT MAY CONCERN FYTOFOAM
The Perfect
Substrate
It gives
me great pleasure to introduce you to FYTOFOAM (known as Fytogreen Foam
in Holland) the leading edge soil amendment made from fully biodegradable
aminoplast resin. Developed in Holland by our partners Verheijen Resins,
b.v., FYTOFOAM and its derivative Fytocell have been extensively used
in a wide variety of horticultural applications including soilless culture
over the last 5 years in Belgium and Holland and more recently in Spain,
Portugal, Germany and Switzerland.
During
the last 12 months FYTOFOAM has been subjected to a rigorous field trial
by STRI at Bingley, Yorkshire, the leading turf research institute,
to test the effects of FYTOFOAM on moisture retention and turf quality
for sports turf rootzones. We attach the full report of these trials
which demonstrate the considerable potential of FYTOFOAM as a substrate
for sports turf surfaces.
We also
commend to you our brochure which explains how the product can be applied
on golf courses, soccer pitches and sports fields and highlights the
many advantages of FYTOFOAM compared with traditional substrates If
you would like to know more about FYTOFOAM please contact our Managing
Director,
Charles
Hudleston.
THE EFFECTS OF FYTOGREEN FOAM ON MOISTURE RETENTION AND TURF QUALITY FOR
SPORTS TURF ROOTZONES FIELD AND GREENHOUSE STUDY For Fytogreen B.V.
SUMMARY
-
A
field trial was conducted to monitor the performance of rootzones
amended with Fytogreen foam, to test whether the foam would enhance
germination and establishment of a healthy turf sward.
-
Following the field trial, a greenhouse dry-down experiment was carried
out using the same rootzones to determine the response of turf swards
to moisture stress, in order to examine whether Fytogreen foam improved
moisture retention and offered benefits for turf quality ? Six rootzones
were tested, comprising sand, a sand/soil mix and a sand/peat mix
and each of these mixes with Fytogreen foam incorporated. In the dry-down
phase, three different irrigation regimes were administered, namely
0, 5 mm and 10 mm of water per week.
-
Fytogreen foam was found to improve grass germination, with the greatest
effect on sand rootzones. On sand rootzones germination was improved
to a level comparable with soil amended rootzones. Considerable improvements
in germination rate were also observed on soil rootzones amended with
Fytogreen
-
Pure sand rootzones were found to support turf of particularly poor
quality. Major improvements were observed on sand plots with Fytogreen
incorporated in the rootzone; these rootzones performed at a level
comparable with rootzones amended with soil and peat. Turf quality
was improved on soil amended plots when Fytogreen is added. There
were no appreciable improvements on peat amended rootzones.
-
Fytogreen improved water retention for all treatments during the first
three weeks of the greenhouse dry-down phase. Fytogreen foam prevented
rapid moisture loss in unwatered lysimeters and in lysimeters watered
with 5 mm per week. Fytogreen accounted for some increase in water
retention for all rootzones, although the effect was most pronounced
and of the greatest duration for sand rootzones.
-
Turf quality measurements during the dry-down period indicate that
Fytogreen slowed the deterioration of turf swards under moisture stress.
The greatest improvements were recorded for unwatered swards and,
in terms of rootzone material, for sand rootzones. Turf quality could
be preserved at an acceptable condition for approximately one week
longer when Fytogreen was added. Fytogreen accounted for only very
minor improvements in the response to drought stress of soil and peat
amended rootzones.
-
The results of this trial suggest Fytogreen has considerable potential
as an alternative rootzone amendment for sports turf surfaces, in
terms of the improvements it offers in grass germination and turf
establishment, and the benefits observed in preserving turf quality
under conditions of moisture stress.

PLATE
1 Installation of the lysimeter pots during the trial construction
INTRODUCTION
Rootzone
materials for sports surfaces are required to be free draining, yet
must also have the capacity to retain enough water to sustain healthy
turfgrass growth. Sand is the principal component of most rootzones
as its relatively coarse particle size characteristics permit free drainage,
even after compaction. To increase water and nutrient retention, rootzones
are typically amended by the addition of material from an organic source
such as peat. However, peat extraction is not a sustainable operation,
and is thus a source of increasing environmental concern. Consequently,
research is needed to examine alternative materials with properties
that offer the same hydrological advantages as traditional amendments.
Fytogreen
foam is a biodegradable foam product manufactured by Fytogreen B.V.
As a rootzone amendment, it is claimed that the foam can enhance drainage
properties, improve aeration and soil structure, and increase water
retention capacity. It is also reported that the foam also has a positive
effect on germination, rooting, nutrient mobilisation and resilience.
A
laboratory
study (STRI report 0066/3) conducted at the STRI examined the soil physical
properties of rootzones amended with Fytogreen foam. The addition of
Fytogreen foam was found to increase capillary porosity and water retention
capacity and decrease hydraulic conductivity and total and air-filled
porosity. The study indicated that Fytogreen foam has potential for
inclusion in rootzones that conform to USGA limits for physical performance.
A field and greenhouse trial was then established to monitor the performance
of rootzones amended with the foam, with two main aims: firstly, to
determine rates of grass establishment and test whether the rootzones
containing Fytogreen foam could maintain a healthy sward; secondly,
to examine the effect of Fytogreen foam during a controlled greenhouse
dry-down phase, to simulate the response of turf swards to drought conditions.
This report describes the methodology of the field and greenhouse trial
and presents the results and interpretations of the measurements that
were taken.
MATERIALS
AND METHODS
Field
study The field trial was conducted on the STRI trial grounds, Bingley,
U.K. There were six experimental treatments, comprising:
1)
Medium sand with no Fytogreen foam
2) Medium sand with 20% Fytogreen foam (by volume)
3) 85: 15 Medium sand to peat mix with no Fytogreen foam
4) 85: 15 Medium sand to peat mix with 15% Fytogreen foam (by volume)
5) 85: 15 Mix of medium sand and sandy loam topsoil with no Fytogreen
foam
6) 85: 15 Mix of medium sand and sandy loam topsoil mix with 15% Fytogreen
foam (by volume)
The
rates of Fytogreen incorporation were based on the results of the laboratory
study (document R0066/3). The sand type used in this study was a 50:50
mix of medium (Rufford 1742) and medium-coarse (Chelford 30); the particle
size distributions of the materials are shown in Table 1. The soil amendment
was a sandy loam topsoil (16% clay, 23% silt, 61% sand) taken from the
STRI trial grounds at Bingley. The peat amendment was a commercially
available Sphagnum moss peat.
TABLE
1 Particle
size distribution (%) and organic matter content (%) of the rootzone
mixes
|
Rootzone
Mix
|
Very
coarse sand (2-1 mm)
|
Coarse
sand (1-0.5)
|
Medium
sand (0.5-0.25)
|
Fine
sand (0.25-0.125)
|
Very
fine sand (0.125-0.05)
|
Silt
and clay (<0.05)
|
Organic
matter (%)
|
|
Pure
sand
|
trace
|
17
|
72
|
11
|
trace
|
trace
|
0.0
|
|
80:20
Sand:Soil*
|
1
|
17
|
63
|
11
|
2
|
6
|
1,2
|
|
80:20
Sand:Peat
|
trace
|
20
|
68
|
10
|
1
|
2
|
2,4
|
*0.6
% was > 2 mm (i.e. gravel)
The
experimental treatments were set out in a factorial randomised block
design with four replications. Each plot was 1 m x 1 m and contained
250 mm of the rootzone over a gravel drainage layer. Six pots (230 mm
diameter) were filled with the respective rootzone material and placed
ca. 5 mm below the surface in each plot (Plate 1), to be used as weighing
lysimeters in the dry-down phase. The trial was sown on 10 August 1999
with perennial ryegrass (Lolium perenne) at 35 g/m2, comprising equal
quantities of three cultivars: Aberelf, Barlinda and Barcrown. The maintenance
procedures are summarised in Table 2. Plates 1 and 2 show general views
of the trial.
Field
measurements
The
following measurements were carried out in accordance with the STRI
standard operating procedures (SOP) given in Appendix I.
-
Visual assessment of grass establishment: measured weekly for the
first four weeks (SOP 301598).
-
Visual assessment of ground cover: measured after 0.5, 1, 2, 3 and
9 months after sowing (SOP 1B1199).
-
Reflectance ratio: measured after 0.5, 1, 2, 3, 6 and 9 months after
sowing - four readings per plot (SOP 301499).
Rainfall
and temperature data coinciding with the trial period are presented
in Appendix II.
Dry-down
phase
The
weighing lysimeters were removed from the trial and set up in the greenhouse
on 5 June 2000. Plate 3 shows the lysimeters in position in the greenhouse.
The following three irrigation treatments were administered to the six
lysimeters from each plot (allowing two replicates): 0 mm (i.e. no irrigation),
5 mm and 10 mm per week. The allotted amount of water was applied on
two separate occasions in each week. A rotation scheme was established
whereby, on each block, every lysimeter was rotated by one row and one
column each week. This was integrated into the design to ensure that
any effect of spatial arrangement (due to potential variations in receipt
of sunlight) would be kept to a minimum. Temperature data for the greenhouse
during the drought stress experiment is given in Appendix II. Because
of the very high temperatures in the greenhouse on the weekend of 17-
18 June all plots received a light syringing of water (approximately
2 mm) to reduce temperatures by evaporation.
TABLE
2 Summary of trial maintenance procedures during the trial
| Fertiliser |
- 10
Aug 1999: 12:6:6 @ 35 g m-2
- 7
September 1999: 12:0:9 @ 20 g m-2
- 21
September 1999: 12:6:6@ 30 g m-2
- 15
October 1999: Maxicrop 6 @ 4 ml m-2
- 1
December 1999: Maxicrop 6 @ 4 ml m-2
- 2
February 2000: Maxicrop 6 @ 4 ml m-2
- 14
March 2000: 12:6:6 @ 35 g m-2 5 May 2000: 12:6:6 @ 25 g m-2
- 23
May 2000: 12:6:6 @ 25 g m-2
|
| Irrigation |
Surface
was heavily watered on nine dates during the establishment phase,
between 31 August and 17 September 1999. |
| Mowing |
The
trial was mown at 35 mm on the 7 and 13 September 1999. The trial
was then mown approximately every 4 days from 17 September at 30
mm until 29 November. Mowing was then carried out on only one occasion
per month in February and March 2000. Through the spring (April
and May 2000) the trial was mown twice weekly at 30 mm. Clippings
were removed each time the trial was mown |
| Other
maintenance |
The
trial was rolled with a 250 kg roller on 31 August and 7 September
1999 to firm the surface. Sand plots and sand and Fytogreen plots
were oversown at 30 g m-2 on 13 September 1999. |
Measurements for dry-down phase
The
following measurements were carried out on all the lysimeters on a weekly
basis for eight weeks. The standard operating procedure for each method
is given in Appendix I.
-
Reflectance ratio: two readings per lysimeter (SOP 301499).
-
Visual appraisal of turf quality: measured where appropriate to supplement
the data set - mean of two assessors (SOP 1B0798).
-
Moisture loss: determined by weighing the lysimeters. Gravimetric
water content was calculated from a sample taken on the final sampling
date (27 July 2000), which was then combined with the weight data
to plot the change in soil moisture of each pot over time.
Statistical
analysis
All
data underwent an analysis of variance test (ANOVA). Where appropriate
the least significant difference (LSD) at the P=0.05 level was calculated
to indicate differences between treatment means.
RESULTS
Field
study
Germination
There
were highly significant effects on germination rate of both amendment
material and Fytogreen application (Table 3). Amendment had a major
influence, with germination occurring fastest on the peat amended rootzones
and slowest on the sand rootzones (Figure 1).
The
influence of Fytogreen was apparent across the range of amendments;
on the sand rootzones it caused an increase in germination rate from
the first assessment date and resulted in considerable improvement over
the next three occasions when germination was measured. The effect of
Fytogreen was minor for the sand/peat rootzones. For sand/soil mixes,
there was no early effect , but major improvements in germination rate
were recorded on 1 and 9 September 1999 (Figure 1). On these occasions
the soil amended plots with Fytogreen out- performed all other treatments.
TABLE
3 Summary of statistical analysis results from field trial showing effect
of amendment and effect of Fytogreen (both averaged over other factors)
|
Date
|
Germination
|
|
%Ground
cover
|
|
Reflectance
Ratio
|
|
|
|
Amendment
|
Fytogreen
|
Amendment
|
Fytogreen
|
Amendment
|
Fytogreen
|
|
18
Aug 99
|
***
|
***
|
***
|
**
|
NS
|
NS
|
|
24
Aug 99
|
***
|
***
|
|
|
|
|
|
1
Sep 99
|
***
|
**
|
***
|
**
|
**
|
**
|
|
9
Sep 99
|
***
|
***
|
|
|
|
|
|
7
Oct 99
|
|
|
***
|
***
|
*
|
**
|
|
4
Nov 99
|
|
|
***
|
***
|
*
|
***
|
|
1
Feb 00
|
|
|
***
|
***
|
NS
|
NS
|
|
5
May 00
|
|
|
***
|
***
|
NS
|
*
|
(Shading
refers to dates when the specified measurement was not taken)
***
P < 0.001
** P < 0.01
* P < 0.05
NS Not Significant
Ground
cover
Significant
effects of Fytogreen and amendment material were recorded throughout
the trial (Table 3). For the amendment material there was a marked difference
between treatments, with sand rootzones consistently having the poorest
ground cover (Figure 2). There was less of a distinction between soil
and peat amended rootzones, although rootzones containing peat consistently
produced the highest level of sward cover.
Highly
significant effects of Fytogreen were observed (Figure 2). Sand rootzones
experienced the greatest improvement in ground cover when Fytogreen
wasincorporated, an increase of ca. 20 percentage points on the latter
four sampling occasions. This improvement resulted in the sand rootzones
amended with Fytogreen out-performing the soil amended mixes and approaching
the cover observed on plots with peat amended rootzones. Soil and peat
amended rootzones were also improved throughout the trial by the incorporation
of Fytogreen, most notably in the case of the soil amended rootzones.
In week 2 (1 September 1999) Fytogreen accounted for a doubling in ground
cover for the soil amended rootzones, and the improvement averages eight
percentage points thereafter.

PLATE
2 View of trial during establishment, showing contrasting stages of
germination between plots



PLATE
3 View of lysimeters in greenhouse during dry-down phase
Dry-down
phase
Moisture
retention
Irrigation input was obviously a major control on water content throughout
the period of drought stress (Table 4), except the first week (08 June
2000). On this occasion the lysimeters had only just been removed from
the field trial, and were therefore of relatively similar moisture content.
Moisture content decreased through the dry-down, with the rate of decrease
inevitably being most rapid for the unwatered lysimeters (Figure 4).
Significant
effects of Fytogreen were recorded in the first three weeks. Inclusion
of Fytogreen foam was found to increase water retention in the early
stage of the dry-down period, most notably on unwatered lysimeters and
those receiving 5 mm of water per week, whilst the effect on 10 mm per
irrigation regime was found to be minor (Figure 4). In terms of rootzone
treatments, the different responses were most striking in the first
three weeks (Figure 5). There was a major amendment effect, with peat
rootzones holding most water and sand holding least; moreover, for each
rootzone type, moisture content was considerably higher and decreased
at a slower rate when Fytogreen was added (Figure 5).
To
account for any influence of the contrasting densities of the rootzone
materials on gravimetric moisture content calculations, a further analysis
was carried out the volume of water contained in the lysimeters on each
measurement date (each lysimeter had a volume of approximately 6.89
litres. The volume of water was calculated from the weight of the lysimeter
minus the oven-dry soil weight and the weight of the plastic container.
The total weight was converted to total volume using a water density
of 1 kg l-1. The statistical analysis confirmed that the significance
of the various effects on each date was identical to the outcome of
the gravimetric data analysis. A summary table of this data is presented
in Table 4.
TABLE
4 Volume of water retained in each lysimeter, giving mean values (in
litres) for each treatment,
averaged over other effects, and LSD's at P <0.05
|
Date
| |
| 08-Jun-00 |
| 15-Jun-00 |
| 22-Jun-00 |
| 29-Jun-00 |
| 06-Jul-00 |
| 13-Jul-00 |
| 20-Jul-00 |
| 27-Jul-00 |
|
Amendment
| Sand |
Soil
|
Peat |
LSD |
| 1.27 |
1.43 |
1.79 |
0.114 |
| 0.90 |
1.08 |
1.35 |
0.131 |
| 0.57 |
0.72 |
0.94 |
0.127 |
| 0.45 |
0.53 |
0.73 |
0.123 |
| 0.56 |
0.61 |
0.80 |
0.111 |
| 0.52 |
0.54 |
0.77 |
0.143 |
| 0.33 |
0.34 |
0.49 |
0.100 |
| 0.35 |
0.33 |
0.50 |
0.081 |
|
Fytogreen
| Fytogreen |
No
Fyto |
LSD |
| 1.64 |
1.35 |
0.093 |
| 1.23 |
0.99 |
0.107 |
| 0.80 |
0.69 |
0.104 |
| 0.60 |
0.54 |
NS |
| 0.68 |
0.64 |
NS |
| 0.65 |
0.58 |
NS |
| 0.38 |
0.39 |
NS |
| 0.39 |
0.40 |
NS |
|
Irrigation
| 0
mm |
5
mm |
10
mm |
LSD |
| 1.50 |
1.48 |
1.51 |
NS |
| 0.90 |
1.08 |
1.34 |
0.098 |
| 0.38 |
0.69 |
1.17 |
0.119 |
| 0.15 |
0.42 |
1.14 |
0.120 |
| 0.14 |
0.46 |
1.37 |
0.139 |
| 0.12 |
0.32 |
1.40 |
0.143 |
| 0.08 |
0.17 |
0.92 |
0.118 |
| 0.07 |
0.21 |
0.90 |
0.118 |
|
Visual Appraisal
Significant
differences were observed between the visual quality of the swards in
terms of irrigation, amendment material and Fytogreen (Table 5; Figures
6 and 7). The impact of moisture stress is clearly apparent; the irrigation
treatment effect was highly significant throughout the experiment, with
the exception of the first two weeks when moisture stress had not begun
to take effect. The visual merit score declined throughout the dry-down
period as moisture stress began to set in and swards began to become
impoverished and die off. Irrigation regime was obviously a crucial
factor in maintaining the sward; the decline in quality over the dry-down
was rapid and severe for the unwatered swards, whilst those irrigated
with 5 mm per week were of reasonable visual merit until the last two
weeks (Figure 6). The lysimeters with the 10 mm per week treatment retained
a sward that at the end of the experiment was only just below the level
of what is regarded as acceptable on the visual appraisal scale (SOP
1B0798, see Appendix I). The effect of Fytogreen on the response of
lysimeters with different irrigation regimes was evident (Figure 6).
The largest effect occurred on the unwatered lysimeters, where Fytogreen
prevented the turf from deteriorating so rapidly. Lysimeters watered
with 5 mm per week displayed an appreciable difference due to Fytogreen,
but the effect on the 10 mm treatments was negligible, a similar pattern
to the moisture retention characteristics previously discussed. Plates
4-6 are views of turf swards at the end of the dry-down; the contrast
in visual quality between irrigation treatments is clear, for each of
the amendments.

PLATE
4 Four sand rootzone lysimeters illustrating the contrast between swards
with and without Fytogreen amendments and between irrigation regimes
(30 June 2000).
Top row =10mm irrigation, bottom row =0mm irrigation. Left column= no
Fytogreen, right column = Fytogreen
TABLE 5 Summary of results of statistical analysis for dry-down, showing
effects of Fytogreen, amendment materials and irrigation regime
|
Date
|
|
|
08-Jun-00
|
|
15-Jun-00
|
|
22-Jun-00
|
|
29-Jun-00
|
|
06-Jul-00
|
|
13-Jul-00
|
|
20-Jul-00
|
|
27-Jul-00
|
|
Amendment
|
Sand
|
Soil
|
Peat
|
LSD
|
|
1.27
|
1.43
|
1.79
|
0.114
|
|
0.90
|
1.08
|
1.35
|
0.131
|
|
0.57
|
0.72
|
0.94
|
0.127
|
|
0.45
|
0.53
|
0.73
|
0.123
|
|
0.56
|
0.61
|
0.80
|
0.111
|
|
0.52
|
0.54
|
0.77
|
0.143
|
|
0.33
|
0.34
|
0.49
|
0.100
|
|
0.35
|
0.33
|
0.50
|
0.081
|
|
Fytogreen
|
Fytogreen
|
No
Fyto
|
LSD
|
|
1.64
|
1.35
|
0.093
|
|
1.23
|
0.99
|
0.107
|
|
0.80
|
0.69
|
0.104
|
|
0.60
|
0.54
|
NS
|
|
0.68
|
0.64
|
NS
|
|
0.65
|
0.58
|
NS
|
|
0.38
|
0.39
|
NS
|
|
0.39
|
0.40
|
NS
|
|
Irrigation
|
0
mm
|
5
mm
|
10
mm
|
LSD
|
|
1.50
|
1.48
|
1.51
|
NS
|
|
0.90
|
1.08
|
1.34
|
0.098
|
|
0.38
|
0.69
|
1.17
|
0.119
|
|
0.15
|
0.42
|
1.14
|
0.120
|
|
0.14
|
0.46
|
1.37
|
0.139
|
|
0.12
|
0.32
|
1.40
|
0.143
|
|
0.08
|
0.17
|
0.92
|
0.118
|
|
0.07
|
0.21
|
0.90
|
0.118
|
|
Moisture
content Visual merit Reflectance ratio Date Irrigation Rootzone Fytogreen
Irrigation Rootzone Fytogreen Irrigation Rootzone Fytogreen 08 Jun 00
NS *** *** * ** ** NS NS NS 15 Jun 00 *** *** *** NS ** * * * NS 22
Jun 00 *** *** ** *** *** *** *** * * 29 Jun 00 *** *** NS *** * * ***
** ** 06 Jul 00 *** *** NS *** *** * *** NS * 13 Jul 00 *** *** NS ***
* * *** ** * 20 Jul 00 *** ** NS *** ** NS *** ** NS 27 Jul 00 *** **
NS *** ** NS *** NS NS There was a significant effect of Fytogreen and
of amendment material through most of the dry-down phase, although the
difference associated with Fytogreen was not significant on the last
two measurement dates. In terms of amendment effects, swards with the
peat amendment had the highest scores (Figure 7) whilst the sand rootzones
supported swards of much poorer quality. The effects of Fytogreen were
substantial. The largest effect was again upon sand rootzones, with
smaller and inconsistent improvements occurring for the amended rootzones
(Figure 7). Plates 4-6 clearly illustrate the effect of Fytogreen on
visual quality of swards at the end of the trial, for each of the rootzones.
The lack of significant effect of Fytogreen in the last two weeks can
be attributed to the fact that by this time most of the swards were
under extreme moisture stress and were thus discoloured and becoming
patchy. Consequently, the differences between lysimeters were becoming
less distinct. The amendment effect was still relatively strong owing
to the substantialdifference in quality between the peat rootzones and
the other rootzones at this late stage (Figure 7). PLATE 5 Four lysimeters
with soil amended rootzones, illustrating the contrast between swards
with and without Fytogreen amendments and between irrigation regimes
on 30th June 2000 (please note pot positions are not the same as for
Plate 4, refer to plate labels). The visual merit data can be used to
estimate how long the condition of a sward can be prolonged to a particular
standard by the addition of Fytogreen foam. A value of five on the visual
merit scale is regarded as the lower limit of acceptable turf quality.
At this level, the time difference between the response curves (from
Figures 6 and 7) gives an estimate of the amount of extra time that
a rootzone amended with Fytogreen will maintain a sward under drought
stress relative to an unamended rootzone. In terms of rootzone medium,
this value was one week for sand rootzones and ca. 2-2.5 days for peat
rootzones. No extra time was apparent at this level for the soil rootzones.
Reflectance ratio The fundamental importance of irrigation regime was
again apparent in the reflectance ratio data, being highly significant
on all occasions except the first two weeks,before the effects of moisture
stress set in. There was a decline in reflectance ratio over the experiment
as moisture stress affected the swards. This decline was strongly influenced
by irrigation and by Fytogreen incorporation (Figure 8). Fytogreen had
most influence on turf quality for the lysimeters receiving no water,
a similar response to that found in the visual merit data, and there
was also some effect on lysimeters watered with 5 mm per week. Significant
results were recorded for amendment and Fytogreen treatments through
the middle period of the dry-down phase (Table 5). The non-significant
results at the end reflect the relative uniformity that occurs when
most swards are undergoing extreme moisture stress. The familiar pattern
of rootzone effects on turf quality emerges from the data; the sand
rootzones performed characteristically poorly, with rapid deterioration
after the second week (Figure 9). The sand lysimeters amended with Fytogreen
fared much better, with considerably slowed deterioration. Rootzones
amended with peat maintained the healthiest swards, although there was
only a minor improvement when Fytogreen was added. Soil amended rootzones
scored intermediately, and were slightly improved by Fytogreen on most
dates. DISCUSSION & CONCLUSIONS Table 6 provides summary data for each
of the measurements over the course of the field trial, showing a comparison
between plots with Fytogreen and those with no Fytogreen, averaged over
the other amendments. Fytogreen was found to improve grass germination
(Table 6). It promoted germination on unamended sand rootzones to a
level approaching those amended with soil. On plots containing soil
amendment, it further stimulated germination by a significant amount.
Fytogreen foam improved turf quality throughout the field trial, as
measured by both visual appraisal and reflectance ratio (Table 6). Pure
sand rootzones were found to score very poorly for all turf characteristics,
and underwent a substantial improvement when Fytogreen foam was added.
The incorporation of Fytogreen improved turf quality to level comparable
to those measured when soil amendments were added, and in several cases
surpassed these. Sand and Fytogreen mixes approached (and with regard
to reflectance ratio, exceeded) the level of quality found with peat
amendments, which is a major improvement given the poor performance
of pure sand rootzones. There was typically a considerable improvement
when Fytogreen is added to soil amended rootzones, whilst the effect
on peat amended rootzones was generally the least pronounced. PLATE
6 Four lysimeters containing peat amended rootzones, illustrating the
contrast between swards with and without Fytogreen and between irrigation
regimes (30 June 2000). TABLE 6 Summary table comparing mean values
for plots with Fytogreen incorporated and plots with no Fytogreen; values
averaged over other amendments. LSD = least significant difference calculated
for the effect of Fytogreen at the P < 0.05 level Date Germination Ground
cover (%) Reflectance ratio Fytogreen No Fyto LSD Fytogreen No Fyto
LSD Fytogreen No Fyto LSD 18 Aug 99 3.0 2.7 0.10 4.5 3.2 0.65 9.4 9.1
NS 24 Aug 99 4.3 3.9 0.16 1 Sep 99 6.6 6.1 0.33 19.7 12.7 3.84 69.1
60.8 5.31 9 Sep 99 8.5 7.9 0.21 7 Oct 99 79.3 64.5 5.18 70.7 66.9 2.43
4 Nov 99 83.8 74.7 2.80 82.4 78.8 1.58 1 Feb 00 92.9 82.3 3.98 68.4
64.7 NS 5 May 00 96.1 87.2 4.77 79.4 74.8 3.72 Table 7 gives summary
data showing the effect of Fytogreen foam for each of the measurements
made during the dry-down period. Fytogreen foam was found to increase
water retention in the first half of the drought phase. During the period,
Fytogreen foam enhanced water retention properties for all treatments,
with the greatest improvement occurring when added to sand. Inclusion
of the foam prevented rapid moisture loss in unwatered lysimeters and
those watered with only 5 mm per week. The patterns that emerge in the
soil moisture data are reflected in the turf quality tests. The results
of these tests indicated that Fytogreen slowed down the deterioration
of swards under moisture stress. This is particularly the case for the
sand rootzones, although the ameliorative properties are apparent for
soil amended rootzones. Significant results were found for both reflectance
ratio and visual appraisal data sets, and the greatest response was
found in swards under the most moisture stress. The data indicate that
addition of Fytogreen can prolongthe quality of swards under drought
stress; for sand rootzones, quality could be preserved at an acceptable
condition for one week longer when Fytogreen was incorporated. TABLE
7 Summary table comparing mean values for lysimeters with Fytogreen
incorporated and lysimeters with No Fytogreen; values averaged over
other amendments. LSD = least significant difference calculated for
the effect of Fytogreen at the P < 0.05 level Date Soil Moisture (%)
Visual appraisal Reflectance ratio Fytogreen No Fyto LSD Fytogreen No
Fytogree n foam LSD Fytogreen No Fyto LSD 08 Jun 00 13.2 10.5 0.64 7.0
6.6 0.29 74.4 74.4 NS 15 Jun 00 10.2 7.9 0.71 7.3 6.9 0.29 78.8 77.6
NS 22 Jun 00 6.8 5.6 0.77 6.9 6.4 0.27 70.5 65.1 4.79 29 Jun 00 5.1
4.4 NS 5.4 5.1 0.30 60.5 53.6 4.16 06 Jul 00 5.7 5.0 NS 4.8 4.6 0.23
48.4 44.2 4.05 13 Jul 00 5.1 4.6 NS 3.9 3.6 0.24 35.0 31.1 3.02 20 Jul
00 3.3 3.2 NS 2.3 2.3 NS 17.3 15.5 NS 27 Jul 00 3.4 3.2 NS 2.6 2.5 NS
17.0 16 NS In relation to the aims of this study it can be concluded
that, in the case of this trial, rootzones containing Fytogreen foam
established and maintained a healthy sward over a period of time, with
the improvements to unamended sand rootzones being particularly substantial.
Secondly, that Fytogreen foam application brought about significant
improvements in the preservation of turf quality under conditions of
drought stress. For the turf properties measured in this study, Fytogreen
performed at a level comparable to traditional amendments. Overall,
the field and greenhouse trials described in this report have demonstrated
that Fytogreen foam has considerable potential as an alternative rootzone
amendment. QUALITY STATEMENT We confirm that this report is a true representation
of the original data collected and that the Standard Operating Procedures
referred to in the STRI Manual of Standard Operating Procedures, and
those relevant to data collection, data preparation, archiving of data
and preparation of reports have been implemented in full. Prepared by:
(Signature and date) Final version checked and reviewed by: (Signature
and date) POLITE REMINDER Please ensure that your Sales/Marketing Department
is aware that this research has been carried out under contract and
that the consent of the STRI must be obtained where information contained
in the report is to be used in advertising or promotional literature.
APPENDIX I STRI STANDARD OPERATING PROCEDURES RELEVANT TO FIELD AND
GREENHOUSE TRIAL ( For further information contact STRI or Greenscape
UK ) APPENDIX II WEATHER DATA DURING FIELD TRIAL AND GREENHOUSE TEMPERATURES
DURING DRY-DOWN PHASE APPENDIX II a) Weekly temperature and rainfall
figures from the STRI trials ground for the period May 1999 to June
2000, when the field trial was in progress Week commencing Maximum temp
(°C) Minimum temp (°C) Rainfall (mm) 02/05/99 15.9 6.6 54 09/05/99 15.7
8.6 27.6 16/05/99 15.1 6.6 0 23/05/99 17 8 14.65 30/05/99 14.9 9 25.9
06/06/99 14.1 7.1 20.85 13/06/99 19.1 10.2 3.3 20/06/99 18.1 8.3 1.05
27/06/99 17.8 8.3 24.45 04/07/99 22.4 14.1 7.6 11/07/99 20 11.5 0.16
18/07/99 18.4 11.9 6.55 25/07/99 20.8 10.4 0 01/08/99 24.8 13.9 20.26
08/08/99 16.7 10 10.25 15/08/99 15.8 9.7 23.3 22/08/99 17.8 11.9 6.3
29/08/99 21.5 12.4 2.85 05/09/99 21.8 10.5 7.65 12/09/99 16.9 7.7 2.35
19/09/99 17.8 9.4 56.15 26/09/99 14.3 9.3 80.65 03/10/99 12.6 4.5 14.15
10/10/99 13.5 5.9 2.45 17/10/99 11.2 5.8 18.55 24/10/99 13.3 6 11.05
31/10/99 12.8 7.4 25.55 07/11/99 10.1 3.8 0.85 14/11/99 6.6 2 2.9 21/11/99
9.9 5 6.65 28/11/99 9 3.8 44.1 05/12/99 8.1 2.5 63.4 12/12/99 5.3 -0.1
46.1 19/12/99 5.1 -1.2 16.9 02/01/00 8.65 2.4 7.05 09/01/00 7 2.1 33.9
16/01/00 5.9 -0.03 0.1 23/01/00 5.83 1.6 3.95 30/01/00 9.63 5.2 38.75
06/02/00 9.2 2.1 22.35 13/02/00 6.9 1 36.9 20/02/00 8 0.9 4.55 Week
commencing Maximum temp (°C) Minimum temp (°C) Rainfall (mm) 27/02/00
8.3 1.6 41.8 05/03/00 11.6 8 26.2 12/03/00 10 3.6 1.15 19/03/00 10.6
2.2 5.25 26/03/00 8.9 0 8.65 02/04/00 8.4 -0.4 16.65 09/04/00 8.4 0.8
38 16/04/00 12 3.3 35.3 23/04/00 14 6.7 23.6 30/04/00 12.8 5.2 0 07/05/00
17 7.3 0 14/05/00 18 6.9 17.2 21/05/00 14.2 4.9 37.4 28/05/00 15.4 7.4
66.7 04/06/00 15.8 7.7 7.25 APPENDIX II b) Temperature data from the
greenhouse during the dry-down phase Fytogreen Foam: Field and Greenhouse
Study
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