diff --git a/fulltext/istex/tei/2FE1BB70A77D356A22B946D72169DC6938FEB254.training.fulltext.tei.xml b/fulltext/istex/tei/2FE1BB70A77D356A22B946D72169DC6938FEB254.training.fulltext.tei.xml
index a9b530b..c64e273 100644
--- a/fulltext/istex/tei/2FE1BB70A77D356A22B946D72169DC6938FEB254.training.fulltext.tei.xml
+++ b/fulltext/istex/tei/2FE1BB70A77D356A22B946D72169DC6938FEB254.training.fulltext.tei.xml
@@ -299,16 +299,18 @@
17
8
7 (42%)
10
6.2
4
19
2
10 (53%)
9
5.8
Total:
189
46
111 (59%)
78
Success rates for long-term
pain relief are calculated as percentages of the number of patients achieving success
- with trial stimulation.
3
Comparison of the Time Interval Between the First
- Operation to the Body Part Experiencing Chronic Pain and SCS
and the Subsequent
- Response to SCS
TIME BETWEEN FIRST
OPERATION AND
IMPLANT
NUMBER
- TRIAL STIMULATION
PAIN RELIEF
LONG-TERM PAIN
RELIEF
AVERAGE
- FOLLOW-UP
PERIOD
(YEARS)
SUCCESS
FAILURE
SUCCESS
- FAILURE
0–3 years
15
14
1
13 (93%)
1
5.2
3–6
- years
34
28
6
23 (82%)
5
5.8
6–9 years
34
- 27
7
15 (56%)
12
6.3
9–12 years
29
28
1
11
- (39%)
17
5.9
12 years
32
23
9
2 (9%)
21
- 5.7
Total:
144
120
24
64 (53%)
56
+ with trial stimulation.
+
+
In the present study eleven species of submerged macrophytes were collected at a with d 0 the capacity (fractal) dimension of the flocs. Solving with d 0 the capacity (fractal) dimension of the flocs. Solving [17] Finding the probability p n (t) in equation (10)
solves
constant depth in a nitrogen and phosphorus rich lake. These were compared with
@@ -329,7 +330,7 @@
the
periphyton composition of a site. Although CASTENHOLZ
(1960) found similar communities
on glass plates and on natural surfaces,
and GODWARD (1934, 1937), WHITFORD
- (1956)
and ODUM (1957) found reasonable
+ (1956)
and ODUM (1957) found reasonable
similarity between communities on aquatic plants and
on artificial substrates, FOERSTER and SCHLICHTING (1965), TIPPETT
(1970), BROWN
(1976) and n ¼ ðL=L p Þ d0 ;
-
equation (3) for L
- and substituting it throughout
equation (1), with the differential dL = ðL p n 1=d
- 0 À1 =d 0 Þ dn,
we can equivalently re-write equation (1) in terms of n as
equation (3) for L and substituting it throughout
equation (1), with the differential dL = ðL p n 1=d 0 À1 =d 0 Þ dn,
+ we can equivalently re-write equation (1) in terms of n
+ as
dt
¼
d 0 G
L d0À3
p
ck a n
3
d 0 À
G
1
2 k b n
d 0 þ1
d 0 L p n
1
d 0 À 1
3Àd0
@@ -218,12 +220,12 @@
the stochastic modeling problem as much as finding the
solution n(t) in
equation (6) solves the deterministic prob-
lem. However,
- the analytical solution to equation (10) can
be difficult to find when the rates f
- a (n) and f b (n) are
functions of the floc state n. Alternatively, a
- numerical
approach that mirrors the assumptions made to write the
forward
- Kolmogorov differential equation can be used. To
accomplish this, we must define
- the inter-event time Dt, the
probability p m
a (t), and the probability p
- m
b (t).
be difficult
+ to find when the rates f a (n) and f b (n) are
functions of the floc state n.
+ Alternatively, a numerical
approach that mirrors the assumptions made to write
+ the
forward Kolmogorov differential equation can be used. To
accomplish this,
+ we must define the inter-event time Dt, the
probability p m
a (t), and the
+ probability p m
b (t).
confidence limit adjusted for the interim analysis 18 for the
differ-
ence hypericum–paroxetine was 1.5 points). In the per protocol
analysis
diff --git a/fulltext/istex/tei/B3490B8637ABC221C150475D7C06AE3BF92D6CEB.fulltext.original.training.fulltext.tei.xml b/fulltext/istex/tei/B3490B8637ABC221C150475D7C06AE3BF92D6CEB.fulltext.original.training.fulltext.tei.xml
index 7a1a98a..df3d576 100644
--- a/fulltext/istex/tei/B3490B8637ABC221C150475D7C06AE3BF92D6CEB.fulltext.original.training.fulltext.tei.xml
+++ b/fulltext/istex/tei/B3490B8637ABC221C150475D7C06AE3BF92D6CEB.fulltext.original.training.fulltext.tei.xml
@@ -101,11 +101,12 @@
reserves on the western
slopes and plains by wide roadside areas,
often
following the valley floor along
creeks and rivers (NSW RLPB
2001). Some
of the highland TSRs contain significant
subalpine
- grasslands (Eddy 2000), whilst
others contain significant riparian wood-
land
- or foothill forest communities. On the
lower slopes, the dominant vegetation
- in
most TSRs is grassy woodland, except TSRs
located along riparian areas such
- as the
Murray River or Billabong Creek, which
support River Red Gum forest
- (Webster
1997; 1999a; 1999b; 2000a; 2000b).
The current dilemma for Rural Land
Protection Board (RLPB) managers is that
TSRs were originally intended for grazing
purposes, however, they often
@@ -588,22 +589,22 @@
we're starting to change the management, it's
quite amazing what is
starting to come back very, very quickly. A lot of the lilies, they come back pretty
quickly; Chocolate
Lily, Vanilla Lily and Onion Orchid are probably the main ones
- that I see (Fig. 5). Today I saw an area of fern I hadn't
- seen
before – then there are the everlasting daisies and the burr daisies. On sites
- where we're getting some of the White Box
regeneration, we are finding little
- saltbushes, orchids and things that you would not imagine could have survived
- considering the use the sites have had over the time. I think lack of cultivation is the
- secret. If the land has never been
cultivated, I think there's a good chance
- of getting it back, but once it's cultivated, its chances are much reduced.
- Michael Mullins from the Riverina board cites the annual forbs as being the plant group
- that is probably the most resilient,
without intervention, along with the wallaby
- grasses and some of the stipas.
But we have not had any good seasons, due to
- drought, since I began this approach here. Also, I know that some species
such as
- the saltbushes are hard to get back in, probably because there's no seed source
- there to bring them back. So seed
sources can be a probem. To counter this,
- we're looking at trialling how to improve some of our isolated patches of
- Kangaroo Grass, north of Moama. We're considering scalping weedy areas and placing
- seed bearing Kangaroo Grass hay
on them.
+ that I see (Fig. 5). Today I saw an area of fern I hadn't seen
before – then
+ there are the everlasting daisies and the burr daisies. On sites where we're
+ getting some of the White Box
regeneration, we are finding little saltbushes,
+ orchids and things that you would not imagine could have survived
considering the
+ use the sites have had over the time. I think lack of cultivation is the secret. If the
+ land has never been
cultivated, I think there's a good chance of getting it
+ back, but once it's cultivated, its chances are much reduced.
Michael Mullins
+ from the Riverina board cites the annual forbs as being the plant group that is probably
+ the most resilient,
without intervention, along with the wallaby grasses and some
+ of the stipas.
But we have not had any good seasons, due to drought, since I began
+ this approach here. Also, I know that some species
such as the saltbushes are hard
+ to get back in, probably because there's no seed source there to bring them back.
+ So seed
sources can be a probem. To counter this, we're looking at trialling
+ how to improve some of our isolated patches of
Kangaroo Grass, north of Moama.
+ We're considering scalping weedy areas and placing seed bearing Kangaroo Grass
+ hay
on them.