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DET FORSTLIGE FORSØGSVÆSEN I DANMARK

THE DANISH FOREST EXPERIMENT STATION STATION DE RECHERCHES FORESTIÉRES DE DANEMARK

DAS FORSTLICHE VERSUCHSWESEN IN DÄNEMARK

B E R E T N I N G E R U D G I V N E V E D D E N F O R S T L I G E F O R S Ø G S K O M M I S S I O N

REPORTS — RAPPORTS - BERICHTE

B IN D X X X V I

HÆFTE 3 ISSN 0367-2174

I N D H O L D

J. N e c k e l m a n n : Dækrodsplanter af nåletræ. Et litteraturstudium og nogle foreløbige resultater fra danske forsøg med rødgran (Picea Abies (L.) H. Karst ) og Sitka (Picea Silchensis (Bong.) Carr.) (Ball-rooted Conifer Plants. A Survey of Literature and Preliminary Results from Danish Experiments with Norway Spruce (Picea Abies (L.) H. Karst.) and Sitka Spruce (Picea Sitchensis (Bong.) Carr.). S. 349—401. (Beretning nr. 304).

B e n t J a k o b s e n : Foreløbige resultater fra unge planteafstandsforsøg i

rødgran. (Preliminary Results from Spacing Experiments in Norway Spruce. S. 403—411. (Beretning nr. 305).

H . H o l s t e n e r - J ø r g e n s e n , V i c e n t e P. V e r a c i o n and C a l i x t o E. Y a o :

Litter Fall Studies in an Irrigation Trial in Norway Spruce. (Strøfalds- undersøgelse i et vandingsforsøg i rødgran). S. 413—432. (Beretning nr. 306).

Rettelse til beretning nr. 282. S. 433.

K Ø B E N H A V N

T R Y K T I K A N D R U P & W U N S C H ’S B O G T R Y K K E R I

1979

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IN AN IRRIGATION TRIAL IN NORWAY SPRUCE

S T R Ø F A L D S U N D E R S Ø G E L S E R I E T V A N D I N G S F O R S 0 G

I R Ø D G R A N

BY

H. H O L S T E N E R -J0 R G E N S E N , VICEN TE P. VERACION, AND CALIXTO E. YAO

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IN T R O D U C T IO N

I n 1944 M ø l l e r p u b lis h e d h is tr e a tis e o n a m o u n ts o f liv in g le a v e s a n d n e e d le s i n s ta n d s o f b e e c h a n d N o rw a y s p ru c e in c o n n e x io n w ith th e a s ­ s im ila tio n a n d th e r e s p ir a tio n in th e s ta n d s . F o r b eech h e m e a s u re d th e to ta l le a f fa ll in se v e ra l s ta n d s ; h o w e v e r, in 10 s p ru c e s ta n d s h e sa m p le d 10 r e p r e s e n ta tiv e tre e s p e r s ta n d a n d w e ig h e d a n d o th e rw is e m e a s u r e d th e to ta l a m o u n t o f n e e d le s o n e a c h tre e .

H is g e n e ra l c o n c lu s io n w a s th a t th e to ta l a m o u n t o f a s s im ila tio n o rg a n s in s ta n d s o f b e e c h o r N o rw a y s p r u c e w ith clo sed c a n o p ie s is i n d e p e n ­ d e n t o f;

1) A ge o f th e s ta n d 2) H e ig h t o f th e s ta n d 3) S ite q u a lity

4) G ra d e o f th in n in g , (p ro v id e d a c o u p le of y e a rs h a v e la p s e d sin c e la s t t h in n in g ) .

C o n c e rn in g 4 ) th i s is in a g re e m e n t w ith h is g e n e ra l s ta te m e n t, b a se d o n a n a n a ly s is o f se v e ra l th in n in g e x p e rim e n ts , t h a t w ith in w id e lim its th in n in g d o es n o t in f lu e n c e th e v o lu m e in c r e m e n t p e r h a . T h is is t r u e in m a n y c a se s, b u t i t d o es n o t h o ld w h e n w o o d d e n s ity is ta k e n in to a c c o u n t.

W ith in c re a s in g th in n in g in te n s ity , M a d s e n , M o l t e s e n , a n d O l e s e n (1978) sh o w ed th a t th e n e t d r y m a t t e r p r o d u c tio n is d e c re a s in g in N o rw a y sp ru c e . T o th e s e n io r a u th o r , M ø l l e r ’s c o n c lu s io n s h a v e sin c e lo n g b e e n a b it p u z z ­ ling, a s a tr e a tm e n t lik e f e rtiliz a tio n o r ir r ig a tio n , w h ic h o n c e r ta in sites r e s u lts in a n in c r e m e n t in c re a s e , n o r m a lly le a v e s th e im m e d ia te im p r e s ­ sio n th a t, a p a r t f r o m b e in g d a r k e r g re e n , n e e d le s a n d le a v e s a re a lso b e ­ c o m in g la rg e r, a n d a f te r o n e o r tw o y e a rs e v e n th e n u m b e r o f o r g a n s seem to be h ig h e r a f te r th e tr e a tm e n t.

T h u s , th e re se e m s to be a m p le r e a s o n to m a k e in v e s tig a tio n s i n w ell d e fin e d e x p e rim e n ts w ith fo r e s t tre e s lik e th e ir r ig a tio n t r i a l u n d e r c o n ­ s id e r a tio n in th is p u b lic a tio n .

R a th e r t h a n m a k in g a n o rm a l e x a m in a tio n o f th e l ite r a tu r e o n litte r fa ll in N o rw a y s p ru c e , th e a u th o r s p r e f e r to p r e s e n t re le v a n t fig u re s fro m th e lite r a tu r e in a ta b le in c o n n e x io n w ith th e d is c u s s io n o f o w n fin d in g s .

STU D Y M E T H O D S a. T h e l a y - o u t o f t h e i r r i g a t i o n trial.

D u rin g th e s p rin g o f 1960 a n a r e a w a s su b d iv id e d in to p lo ts s u r r o u n d e d b y p la te s o f a b e s to s -c e m e n t d u g in to th e soil. T h e p la te s o v e rla p b y a t le a s t 6 c m a n d th e o v e rla p is se ale d w ith a s p h a lt. T h e soil, a c la y e y m o - ra in e -s o il, is fre e ly d ra in e d . N o g ro u n d w a te r ta b le h a s b e e n o b se rv e d w ith in

Det fo rstlig e F o rsø g sv æ sen . XNX.VI. H. 3. 11. o k to b e r 1979.

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th e to p 2.5 m . T h u s , th e p lo ts m a y be re g a r d e d a s se lf-c o n ta in e d , f r e e ly d r a in e d v essels.

A lso in th e s p r in g o f 1960, 4 -y e a r-o ld N o rw a y s p ru c e s w e re p l a n te d , th e sp a c in g b ein g 0 .9 3 X 1 -0 0 m . S u r r o u n d in g th e p lo ts tw o ro w s o f N o r ­ w a y s p r u c e w e re p la n te d as iso la tio n . E a c h p lo t m e a s u r e s 45.5 m 2.

N 1

I • trees in isolationstrip

J

° tria l trees I

F i g u r e 1. The lay-out of the trial.

F i g u r 1. Forsøgsplan.

D u rin g th e s p r in g o f 1974 a n ir r ig a tio n t r ia l w a s e s ta b lis h e d in t h e s ta n d , w h ic h by th e n h a d a c o m p le te ly clo sed c a n o p y . T h e m e a n h e i g h t o f th e s ta n d w a s 5.4 m . T h e la y -o u t m a y be se e n fro m F ig u r e 1. T h e t r i a l c o m p ris e s th e fo llo w in g tr e a tm e n ts —

(a ) 2 c o n tro l p lo ts

(b ) 2 p lo ts o n w h ic h , fro m A p ril 1 to S e p te m b e r 30, p a r t of th e s u r f a c e o f th e g r o u n d is s c re e n e d o ff b y p la te s , so t h a t 73.3 % o f th e t h r o u g h - fa ll is d iv e rte d . T h e q u a n tity o f c a r r ie d - o ff w a te r is m e a s u re d .

(c ) 2 p lo ts w h e re , in th e sa m e p e rio d , 20 m m o f w a te r is s u p p lie d to t h e soil w h e n e v e r th e d iffe re n c e b e tw e e n p r e c ip ita tio n -j- ir r ig a tio n w a t e r a n d a c o m p u te d e v a p o ra tio n c u rv e ( H o l s t e n e r - J ø r g e n s e n a n d H o l m s - g a a r d , 1975) ex ceed s 40 m m . H e r e a f te r c a lle d i / 2 i r r i g a t e d .

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(d ) 2 p lo ts w h e re , in th e sa m e p e rio d , 40 m m o f w a te r is s u p p lie d w h e n ­ ev er th e d iffe re n c e m e n tio n e d u n d e r (c ) ex c eed s 40 m m . H e re a fte r c a lle d 1 / 1 i r r i g a t e d .

T h e ir r ig a tio n is m a d e b y tr ic k le - ir r ig a tio n (se e H o l s t e n e r - J ø r g e n s e n a n d J o h a n s e n , 1975).

P r e lim in a r y r e s u lts o f f ie ld -m e a s u re m e n ts h a v e b een p u b lis h e d (H o l ­ s t e n e r - J ø r g e n s e n a n d H o l m s g a a r d , 1 9 7 7 ).

b. T h e m e t h o d u s e d to o b t a i n l i t t e r s a m p l e s .

5 p la s tic f u n n e ls w e re p la c e d , ev e n ly sp a c e d , d ia g o n a lly b e tw e e n R ow 1 a n d R ow 2 a n d 5 f u n n e ls lik e w ise betw reen R o w 6 a n d Rowr 7. T h e ro w s r u n n o r th - s o u th a n d th e y w e re n u m b e re d fro m th e w e s te r n edge. T h e f u n n e ls u s e d w e re o f tw o d ia m e te r c la sse s, 140 m m a n d 175 m m . T h e fu n n e ls wrere p ro v id e d w ith a w ir e s u p p o r t a n d th e ir o u tle ts w e re fu r n is h e d w ith a n y lo n s c re e n to av o id w a te r a c c u m u la tio n . T h e a v e ra g e fu n n e l- a r e a p e r p lo t w a s 0.192 m 2, th u s re p r e s e n tin g 0.42 % o f p lo t a r e a s o f 45.5 m -.

T h e f u n n e ls wrere p la c e d in th e p lo ts o n J u n e 7, 1977. T h e y w e re e m p ­ tie d on A u g u s t 6, O c to b e r 10, D e c e m b e r 21, 1977 a n d M a rc h 28, J u n e 2, 1978 a t w h ic h d a te th e in v e s tig a tio n w a s fin is h e d a f te r a lto g e th e r 360 d a y s.

c. L a b o r a t o r y m e t h o d s .

I n th e la b o r a to r y th e s a m p le s w e re a ir d r ie d a n d d iv id e d in to a ) n e e d ­ les a n d b ) o th e r th in g s (tw ig s, b a rk , c o n es a n d o th e r m a t t e r ) . E a c h c a te ­ g o ry w a s w e ig h e d a f te r k iln - d r y in g (6 0 ° C ). T h e y w e re g r o u n d (W ile y -m ill, 20 m e s h sieve) a n d a s u b -s a m p le w a s d r y a sh e d . T h e a s h w a s d isso lv e d in HC1, a n d a f te r p r e c ip ita tin g o f silic a, th e so lu te w a s a n a ly s e d fo r P (c o lo rim e tric , n itr ic a c id — m o ly b d a te — v a n a d a te ) , K (f la m e p h o to m e ­ t r ic ) , a n d Mg (a to m ic a b s o r p tio n s p e c tr o p h o to m e tr y ) . N wra s d e te rm in e d b y a s e m i-m ic ro K je ld a h l m e th o d .

R E S U L T S a. W e i g h t s o f l i t t er .

T a b le 1 show 's g ra n d m e a n s w ith th e ir s ta n d a r d e r r o r s f o r (1 ) s p ru c e n e e d le s a n d (2 ) o th e r th in g s a t th e d if f e r e n t s a m p lin g d a te s . S ta n d a r d e r r o r s a re b a se d o n re s id u a ls a f te r a n a ly s e s o f v a ria n c e s , re m o v in g v a r ­ ia n c e s d u e to ( a ) b lo c k s, (b ) tr e a tm e n ts , a n d (c ) fu n n e l p o s itio n in th e p lo ts. It m a y b e seen th a t, w h e re a s th e n e e d le fa ll is re a s o n a b le ev en on a n a re a -b a s is , o th e r th in g s a re fa llin g r a t h e r u n e v e n . T h is tr e n d is n o t u n e x p e c te d a n d is k n o w n fro m o th e r stu d ie s.

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T a b l e 1. Survey of m eans and stan d ard e rro rs of m eans for litte r com ponents.

T a b e I 1. Oversi gt o v e r m i d d e l v æ r d i e r f or s t r ø k o mp o n e n t er n e og mi dde t f e j l på mi d d e l v ær d i e r .

D ate o f co llectio n

J n d s a m - li n g s d a t o

S p ru c e needles O ther th in g s

Mean g /m 2

S ta n d a rd e rro r M ean

g /m 2

S ta n d a rd e r ro r g /m 2

R ø d g r a n n å l e

re la tiv e g /m 2

A n d r e ti n g

re la tiv e

M i d d e l g / m 2

M i d d e l f e j l M i d d e l

g / m 2

M i d d e l f e j l

g / m - r e l a t i v g / m - r e l a t i v

6/8 -1977 60.73 2.257 3.72 11.83 0.729 6.16

10/10-1977 52.38 1.616 3.09 34.42 12.667 36.80

21/12-1977 79.65 2.121 2.66 19.57 4.322 22.08

28/3 -1978 52.77 1.324 2.51 17.40 1.240 7.13

2/6 -1978 112.44 5.395 4.80 11.70 0.197 1.68

M ean d a ily l itte r fa ll in th e 5 s a m p lin g p e r io d s c a n be se e n fro m T a b le 2. T h e r e is a s ig n if ic a n t re s p o n s e to tr e a tm e n ts (0.01 < p < 0 .0 5 ). T h e g e n e ra l tr e n d is t h a t th e a m o u n t o f l i t t e r fa ll is ris in g w ith im p ro v e d w a te r b a la n c e ; h o w e v e r, th e r e is no d if fe re n c e b e tw e e n 1 /2 ir r ig a te d a n d 1 /1 ir r ig a te d .

T a b l e 2. Average litte r fall p e r day in the collection perio d s, g /m 2.

SN = spruce needles; OT = o ther things.

T a b . e l 2. Gennemsni t l i gt dagligt st røfal d i de enkel te i n dsaml i ngspe ri ode r, g / m 2.

SN = rødgrannål e; OT = andre ting.

Period. N u m b er

o f d ay s F ra c tio n C ontrol — T h ro u iih - fa ll ‘ l / 2 - i r r i -

g ated l / l - i r r i - gated

Mean

P e r i o d e A n t a l

d a g e F r a k t i o n K o n t r o l S k æ r m e t 1/2 v a n d e t 1/1 v a n d e t M i d d e l

June 7, 1977 to

Aug. 6, 1977 60 SN

OT Sum

1.090 0.252 1.342

0.735 0.161 0.896

1.120 0.197 1.317

1.104 0.179 1.283

1.012 0.197 1.209 Aug. 6, 1977 to

Oct. 10, 1977 65

SN OT Sum

0.705 0.418 1.123

0.738 0.221 0.959

0.822 0.430 1.252

0.958 1.048 2.006

0.806 0.529 1.335 Oct. 10, 1977 to

Dec. 21, 1977 72

SN OT Sum

0.860 0.374 1.234

1.131 0.204 1.335

1.162 0.299 1.461

1.272 0.210 1.482

1.106 0.272 1.378 Dec. 21, 1977 to

M arch 28, 1978 97 SN

OT Sum

0.529 0.173 0.702

0.454 0.127 0.581

0.593 0.226 0.819

0.600 0.191 0.791

0.544 0.179 0.723

M arch 28, 1978 to SN 1.785 1.246 2.020 1.762 1.703

June 2, 1978 66 OT 0.161 0.120 0.214 0.215 0.178

Sum 1.946 1.366 2.234 1.977 1.881

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T h e r e is a h ig h ly s ig n if ic a n t in te r a c tio n b e tw e e n s a m p lin g p e rio d s a n d l i tte r f a ll (p < 0 .0 0 1 ), w h ic h is d u e to d if f e r e n t a m o u n ts of l itte r fa ll fro m p e rio d to p e rio d a n d to v a ry in g r a tio s b e tw e e n n e e d le fa ll a n d fa ll o f o th e r th in g s . T h e fa ll o f n e e d le s is h ig h e s t in th e p e rio d fr o m M a rc h 28 to J u n e 2, 1978 ( s p r in g — e a rly s u m m e r ) a n d lo w e st in th e p e rio d D e c e m b e r 21, 1977 to M a rc h 28, 1978 ( w in te r ) . I t is n o ta b le th a t, f ro m A u g u s t 6 to O c ­ to b e r 10, 1977 a n d fro m O c to b e r 10 to D e c e m b e r 21, 1977 n e e d le fa ll is r e la tiv e ly h ig h in th e p lo ts w ith c u t-d o w n th r o u g h f a ll c o m p a re d w ith o th e r p lo ts, w h ic h is p ro b a b ly d u e to th e a r tif ic ia l d ro u g h t, in good a c c o rd a n c e w ith th e f in d in g s by, a m o n g o th e rs , B o r n e b u s c h (1 9 3 7 ) a n d M o r k (1 9 4 2 ).

T h e fa ll o f o th e r th in g s is h ig h e s t d u r in g la te s u m m e r — a u tu m n a n d lo w e st d u r in g w in te r a n d s p r in g — e a rly s u m m e r. I t m u s t be k e p t in m in d th a t th e s a m p lin g e r r o r f o r o th e r th in g s is g re a t. T h e s ta n d a r d e r r o r of th e g r a n d m e a n in T a b le 2 is 13.4 % , so n o t to o m u c h im p o r ta n c e s h o u ld be a tta c h e d to th e d if fe re n c e s m e n tio n e d .

T h e c u m u la tiv e litte r f a ll d u r in g th e 360 d a y s ’ p e rio d u n d e r in v e s t­

ig a tio n c a n b e se e n in T a b le 3 a n d F ig u r e 2. T h is ta b le , as w e ll a s th e fig u re , re fle c ts th e d iffe re n c e s b e tw e e n s a m p lin g p e rio d s a lre a d y m e n tio n e d . T h e n e e d le fa ll d u r in g th e w h o le p e rio d is a r o u n d 4 to n s of d r y m a tte r p e r h a in th e ir r ig a te d p lo ts , 3.4 to n s in c o n tro l p lo ts, a n d 3.0 to n s in th e

T a b l e 3. Cumulative litte r fall, g /m 2.

SN = sp ru ce needles; OT = o ther things.

T a b e l 3. Akkumul er et strøfald, g / m 2.

SN = rødgrannål e; OT = andr e ting.

P e rio d F ra c tio n C ontrol —T h ro u g h fa ll 1/2 irrig a te d 1/1 irrig a te d

P e r i o d e F r a k t i o n K o n t r o l S k æ r m e t 1/2 v a n d e t 1/1 v a n d e t

June 7, 1977 SN (55.38 44.10 67.20 66.23

to Aug. 6, 1977 OT 15.10 9.65 11.83 10.73

Sum 80.48 53.75 79.03 76.96

June 7, 1977 SN ■ 111.23 92.05 120.63 128.53

to Oct. 10, 1977 OT 42.29 24.04 39.78 78.88

Sum 153.52 116.09 160.41 207.41

June 7, 1977 SN 173.17 173.48 204.29 220.13

to Dec. 21, 1977 OT 69.19 38.74 61.34 94.02

Sum 242.36 212.22 265.63 314.15

June 7, 1977 SN 224.50 217.53 261.81 278.30

to M arch 28, 1978 OT 85.98 51.07 83.30 112.57

Sum 310.48 268.60 345.11 390.87

June 7, 1977 SN 342.34 299.79 395.16 394.61

to June 2, 1978 OT 96.62 58.97 97.41 126.73

Sum 438.96 358.76 492.57 521.34

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g / m

2

t / h a

5

0

days

F i g u r e 2. The cum ulative litter fall in the study period.

F i g n r 2. Det s u m m e r e d e st røf ai d i u nde rsøgel sespe ri ode n ( se i øvr i gt tabel- t ekster).

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s h ie ld e d p lo ts . T h e fa ll o f o th e r th in g s is 1.3 to n s p e r h a in 1 /1 ir r ig a te d p lo ts , a r o u n d 1.0 to n i n 1 /2 ir r ig a te d a n d c o n tro l p lo ts, a n d 0.6 to n in s h ie ld e d p lo ts . T h e to ta l litte r fa ll is a r o u n d 5.2 to n s p e r h a in 1 /1 i r r i ­ g a te d p lo ts, 4.9 to n s i n 1 /2 ir r ig a te d p lo ts , 4.4 to n s in c o n tr o l p lo ts, a n d 3.6 to n s in sh ie ld e d p lo ts . I t s h o u ld be n o tic e d t h a t th e la s t tw o d iffe re n c e s b e tw e e n 1 /2 ir r ig a te d a n d 1 /1 ir r ig a te d o rig in a te m a in ly f ro m th e la rg e a m o u n t o f o th e r th in g s in th e 1 /1 ir r ig a te d p lo ts co lle c te d in th e p e rio d A u g u s t 6 to O c to b e r 10, 1977.

b. N u t r i e n t c o n c e n t r a t i o n s in t h e l i t t er .

A su rv e y o f th e n u tr ie n t c o n c e n tr a tio n s in th e tw o c o m p o n e n ts o f th e l i t t e r is s h o w n in T a b le 4.

T a b l e 4. C oncentrations (% ) of ash and n u trien ts in the litte r fall com ponents at the differen t sam pling dates.

T a b e l 4. I n d h o l d e t ( % ) af aske og næri ngss t off er i strøfaldets f r akt i oner p å de forskel lige indsamli ngsdage.

L itte r co m p o n en t

C ontrol —T h ro u g h fa ll

S t r ø - f r a k t i o n

E lem ent 6/8-77 10/10-77 21/12-77 K o n t r o l

28/3-78 2/6-78 6/8-77 10/10-77 21/12-77 S k æ r m e t

28/3-78 2/6-78

E l e m e n t 6/ 8 -77 1 0 /1 0 -7 7 2 1 / 1 2 -77 28 /3 -7 8 2 / 6 -7 8 6 /8 - 7 7 10 /10 -77 2 1 /1 2 -7 7 2 8 /3 -7 8 2/6 -7 8

Spruce Ash 6.9 8.4 6.5 6.5 6 .2 7.3 8.5 6.8 7.2 6.4

needles N 1.32 1.24 1.10 1.45 1.24 1.21 1.16 0.97 1.30 1.16

Rødqran- nåle

P 0.16 0.15 0.17 0.16 0.16 0.16 0.15 0.16 0.16 0.16

K 0.32 0.38 0.45 0.37 0.61 0.34 0.39 0.36 0.30 0.57

Mg 0.09 0.13 0.10 0.10 0.10 0.10 0.16 0.10 0.09 0.09

Otlier Ash 16.3 16.6 16.5 25.6 23.9 29.4 20.0 20.1 26.7 29.6

things N 1.88 1.62 1.51 1.93 1.83 1.94 1.90 1.37 2.37 1.76

An d r e P 0.23 0.21 0.34 0.26 0.29 0.30 0.23 0.26 0.33 0.29

ting K 0.31 0.45 0.29 0.24 0.36 0.27 0.41 0.33 0.16 0.29

Mg 0.14 0.19 0.16 0.12 0.11 0.13 0.18 0.12 0.10 0.12

T a b l e 4 (co n tin u ed ).

T a b e l 4 (fort sat) .

L itte r

com ponent 1 /2 irrig a te d 1/1 irrig a te d

S t r ø ­ f r a k t i o n

E le m e n t 6/8-77 10/10-77 21/12-77

1/2 v a n d e t

28/3-78 2/6-78 6/8-77 10/10-77

i f l

21/12-77 v a n d e t

28/3-78 2/6-78

E l e m e n t 6 / 8 - 7 7 1 0 /1 0- 7 7 21 /1 2-7 7 28 /3 -7 8 2/6-78 6 /8 - 7 7 1 0 / 1 0 -77 2 1 /1 2 -7 7 28 /3 -7 8 2/6 -7 8

Spruce Ash 7.9 8.9 7.1 7.8 7.4 7.6 9.6 8.0 8.3 6.8

needles N 1.23 1.15 1.01 1.43 1.12 1.40 1.24 1.18 1.34 1.24

Rødgr an ­ P 0.16 0.16 0.17 0.16 0.18 0.17 0.17 0.17 0.17 0.19

nåle K 0.37 0.40 0.42 0.33 0.65 0.35 0.37 0.36 0.30 0.60

Mg 0.10 0.14 0.10 0.10 0.10 0.10 0.14 0.10 0.10 0.10

O ther Ash 19.2 22.3 19.8 34.1 33.9 22.7 54.2 23.3 36.7 33.8

things N 1.87 1.64 1.45 2.07 2.16 1.85 1.78 1.90 2.06 2.35

An d r e P 0.31 0.25 0.27 0.35 0.37 0.29 0.34 0.37 0.41 0.29

ting K 0.29 0.47 0.29 0.20 0.37 0.28 0.30 0.30 0.19 0.31

Mg 0.13 0.17 0.13 0.12 0.15 0.13 0.19 0.13 0.13 0.11

Det fo rs tlig e F o rsø g sv æ sen . XXXVI. H . 3. I I . o k to b e r 1979. 6

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In th e s p ru c e n e e d le s, c o n c e n tra tio n s a r e v a ry in g -with th e s a m p lin g p e rio d s . G e n e ra lly th e d iffe re n c e s a re h ig h ly s ig n if ic a n t (p < 0 .0 0 1 ). T h e o n ly e x c e p tio n is i n th e P -c o n c e n tra tio n s (0.01 < p < 0 .0 5 ).

T h e tr e a tm e n ts h a v e a h ig h ly s ig n if ic a n t in flu e n c e o n th e a s h c o n c e n ­ tr a tio n s (p < 0 .0 0 1 ). T h e a s h c o n c e n tr a tio n s a re h ig h e r in th e n e e d le s in th e tr e a te d p lo ts t h a n in th e c o n tro ls .

A lso N - c o n c e n tr a tio n s i n th e n e e d le s a r e s ig n if ic a n tly in flu e n c e d b y tr e a tm e n ts (0.001 < p < 0 .0 1 ). I n th is c a se sh ie ld e d p lo ts a n d 1 /2 i r r i ­ g a te d p lo ts h a v e , o n a n a v e ra g e , lo w e r c o n c e n tr a tio n s t h a n c o n tr o ls a n d 1 /1 ir r ig a te d p lo ts . T h e o v e ra ll d iffe re n c e b e tw e e n th o s e tw o g ro u p s is 0.10 % N.

T h e tr e a tm e n ts h a v e h a d a s ig n ific a n t in flu e n c e o n P -c o n c e n tra tio n s in th e n e e d le s (0.001 < p < 0 .0 1 ). T h e g e n e ra l tr e n d is t h a t P -c o n c e n tra - tio n s a re h ig h e r i n th e ir r ig a te d p lo ts th a n in th e c o n tro ls a n d th e sh ie ld e d p lo ts . T h e m e a n d iffe re n c e b e tw e e n th o s e g ro u p s is 0.009 % P .

T h e d e te r m in a tio n o f K -c o n c e n tra tio n s i n f a lle n n e e d le s is o f m a r g in a l in te r e s t o n ly , a s m o s t o f th e p o ta s s iu m in p l a n t tis s u e is w a te r s o lu b le a n d m a y be w a s h e d o u t o f th e tis s u e b y th e r a in f a ll, b o th w h e n th e tis s u e is aliv e a n d w h e n , a s in litte r , i t is d e a d ( T a m m 1951, M a d g w i c k a n d O v i n g - t o n 1 9 5 4 ). T h e r e is no s ig n if ic a n t d iffe re n c e b e tw e e n K -c o n c e n tra tio n s (0.05 < p < 0 .1 0 ), b u t th e g e n e ra l te n d e n c y is t h a t c o n c e n tr a tio n s a re lo w e r in th e sh ie ld e d p lo ts a n d th e 1 /1 ir r ig a te d p lo ts th a n i n th e c o n ­ tr o ls a n d th e 1 /2 ir r ig a te d p lo ts.

M g -c o n c e n tra tio n s in n e ed le l i t t e r seem to be f u lly in d e p e n d e n t o f th e tr e a tm e n ts .

C o n c e rn in g th e se c o n d litte r c o m p o n e n t, o th e r th in g s , th e v a r ia tio n in n u t r i e n t c o n c e n tr a tio n s is c o n s id e ra b le , a n d th e r e a re n o g e n e ra l s ig n ific a n t tr e n d s . T h e r e a re s ig n ific a n t d iffe re n c e s b e tw e e n s a m p lin g d a te s fo r N -co n ­ c e n tr a tio n s (0.001 < P < 0 .01), f o r K -c o n c e n tra tio n s ( p < 0 .0 0 1 ), a n d fo r M g -c o n c e n tra tio n s (p < 0 .0 0 1 ). T r e a tm e n ts h a v e h a d no s ig n ific a n t i n ­ flu e n c e o n th e c o n c e n tra tio n s .

c. A m o u n t s o f n u t r i e n t s r e t u r n e d w i t h t h e l i t t er .

T a b le s 5 to 9 sh o w th e c u m u la tiv e n u t r i e n t c o n te n t in th e l itte r d u r in g th e in v e s tig a tio n p e rio d , a n d in F ig u r e 3 th e fig u re s fro m T a b le 6 (N -con- te n t in l i t t e r f a ll) a r e p lo tte d a g a in s t tim e to i l lu s tr a te th e r e t u r n of N to th e soil s u rfa c e .

T h e re is a g e n e ra l tr e n d in th e fig u re s w h ic h is in a g re e m e n t w ith th e tr e n d s in th e b a s ic f ig u re s on w h ic h th e y a re fo u n d e d , w e ig h t o f l itte r a n d n u tr ie n t c o n c e n tr a tio n s i n litte r. T h e a s h a n d n u t r i e n t r e t u r n wTith th e litte r is lo w e st in th e sh ie ld e d p lo ts, c o n tro ls a r e in te r m e d ia te , a n d ir r ig a te d p lo ts

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T a b e l 5. Ak k u mu l e r e t i n d h o l d af aske i strøfaldet, g / m 2.

SN = r ødgrannål e; OT = andr e ting.

T a b l e 5. Cumulative content of ash in litter fall, g /m 2.

SN = spruce needles; OT = other things.

P e rio d F ra c tio n C ontrol —T h ro u g h fa ll 1 /2 ir rig a te d 1/1 irrig a te d

P e r i o d e F r a k t i o n K o n t r o l S k æ r m e t 1/2 v a n d e t 1/1 v a n d e t

June 7, 1977 SN 4.51 3.23 5.30 5.01

to Aug. 6, 1977 OT 2.47 2.84 2.27 2.43

Sum 6.98 6.07 7.57 7.44

June 7, 1977 SN 8.35 7.28 10.08 10.98

to Oct. 10, 1977 OT 6.99 5.72 8.51 39.35

Sum 15.34 13.00 18.59 50.33

Ju n e 7, 1977 SN 12.40 12.82 16.05 18.29

to Dec. 21, 1977 OT 11.43 8.67 12.79 42.88

Sum 23.83 21.49 28.84 61.17

Ju n e 7, 1977 SN 15.72 16.00 20.54 23.12

to M arch 28, 1978 OT 15.72 11.96 20.29 49.68

Sum 31.44 27.96 40.83 72.80

Ju n e 7, 1977 SN 22.98 21.26 30.46 31.03

to June 2, 1978 OT 18.26 14.30 25.07 54.46

Sum 41.24 35.56 55.53 85.49

T a b l e 6. Cum ulative co n ten t of N in litte r fall, g /m 2.

SN = spruce needles; OT = o th er things.

T a b e l 6. A k k u mu l e r e t i n d h o l d af N i strøfaldet, g / m 2.

SN = rødgrannål e; OT = a n d r e ting.

P e rio d F ra c tio n C ontrol —T h ro u g h fa ll 1 /2 irrig a te d 1/1 irrig a te d

P e r i o d e F r a k t i o n K o n tr o l S k æ r m e t 1/2 v a n d e t 1/1 v a n d e t

June 7, 1977 SN 0.86 0.53 0.83 0.93

to Aug. 6, 1977 OT 0.28 0.19 0.22 0.20

Sum 1.14 0.72 1.05 1.13

June 7, 1977 SN 1.43 1.09 1.44 L70

to Oct. 10, 1977 OT 0.72 0.46 0.68 1.41

Sum 2.15 1.55 2.12 3.11

June 7, 1977 SN 2.11 1.88 2.28 2.78

to Dec. 21, 1977 OT 1.13 0.66 0.99 1.70

Sum 3.24 2.54 3.27 4.48

Ju n e 7, 1977 SN 2.85 2.45 3.10 3.56

to M arch 28, 1978 OT 1.45 0.95 1.44 2.08

Sum 4.30 3.40 4.54 5.64

Ju n e 7, 1977 SN 4.31 3.40 4.59 5.00

to June 2, 1978 OT 1.64 1.09 1.74 2.41

Sum 5.95 4.49 6.33 7.41

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T a b e l 7. A k k u mu l e r e t i n d h o l d af P i s t r øf aldet, g / m 2.

SN = rødgrannål e; OT = andr e ting.

T a b l e 7. Cumulative content of P in litter fall, g /m 2.

SN = spruce needles; OT = other things.

P e rio d F ra c tio n • C ontrol —T h ro u g h fa ll 1/2 ir rig a te d 1/1 irrig a te d

P e r i o d e F r a k t i o n K o n t r o l S k æ r m e t 1 /2 v a n d e t 1 /1 v a n d e t

June 7, 1977 SN 0.10 0.07 0.11 0.11

to Aug. 6, 1977 OT 0.03 0.03 0.04 0.03

Sum 0.13 0.10 0.15 0.14

Ju n e 7, 1977 SN 0.17 0.14 0.19 0.22

to Oct. 10, 1977 OT 0.09 0.06 0.11 0.26

Sum 0.26 0.20 0.30 0.48

June 7, 1977 SN 0.27 0.27 0.33 0.37

to Dec. 21, 1977 OT 0.18 0.10 0.17 0.32

Sum 0.45 0.37 0.50 0.69

Ju n e 7, 1977 SN 0.35 0.34 0.42 0.47

to M arch 28, 1978 OT 0.42 0.14 0.25 0.40

Sum 0.77 0.48 0.67 0.87

June 7, 1977 SN 0.54 0.47 0.65 0.69

to June 2, 1978 OT 0.45 0.16 0.30 0.44

Sum 0.99 0.63 0.95 1.13

T a b l e 8. Cum ulative co n ten t of K in litte r fall, g /m 2.

SN = spruce needles; OT = o th e r things.

T a b e l 8. A k k u mu l e r e t i n d h o l d af K i strøf aldet, g / m 2.

SN = rødgrannål e; OT = a n d r e ting.

P e rio d F ra c tio n C ontrol —T h ro u g h fa ll 1/2 irrig a te d 1/1 irrig a te d

P e r i o d e F r a k t i o n K o n t r o l S k æ r m e t 1/2 v a n d e t 1 / 1 v a n d e t

June 7, 1977 SN 0.21 0.15 0.25 0.23

to Aug. 6, 1977 OT 0.05 0.03 0.03 0.03

Sum 0.26 0.18 0.28 0.26

June 7, 1977 SN 0.38 0.34 0.46 0.46

to Oct. 10, 1977 OT 0.17 0.09 0.16 0.23

Sum 0.55 0.43 0.62 0.69

June 7, 1977 SN 0.66 0.63 0.81 0.79

to Dec. 21, 1977 OT 0.25 0.14 0.22 0.28

Sum 0.91 0.77 1.03 1.07

June 7, 1977 SN 0.85 0.76 1.00 0.96

to M arch 28, 1978 OT 0.29 0.16 0.26 0.32

Sum 1.14 0.92 1.26 1.28

June 7, 1977 SN 1.57 1.23 1.87 1.66

to June 2, 1978 OT 0.33 0.18 0.31 0.36

Sum 1.90 1.41 2.18 2.02

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T a b e l 9. Ak k u mu l e r e t i n d h o l d af Mg i strøfaldet, g / m 2.

SN = rødgrannål e; OT = andr e ting.

T a b l e 9. Cumulative content of Mg in litter fall, g /m 2.

SN = spruce needles; OT = other things.

P e rio d F ra c tio n C ontrol — T h ro u g h fa ll 1/2 irrig a te d 1/1 irrig a te d

P e r i o d e F r a k t i o n K o n t r o l S k æ r m e t 1 / 2 v a n d e t 1 / 1 v a n d e t

June 7, 1977 SN 0.06 0.04 0.07 0.07

to Aug. 6, 1977 OT 0.02 0.01 0.02 0.01

Sum 0.08 0.05 0.09 0.08

June 7, 1977 SN 0.12 0.12 0.15 0.15

to Oct. 10, 1977 OT 0.07 0.04 0.07 0.14

Sum 0.19 0.16 0.22 0.29

June 7, 1977 SN 0.18 0.20 0.23 0.24

to Dec. 21, 1977 OT 0.11 0.06 0.10 0.16

Sum 0.29 0.26 0.33 0.40

June 7, 1977 SN 0.23 0.24 0.29 0.30

to M arch 28, 1978 OT 0.13 0.07 0.13 0.18

Sum 0.36 0.31 0.42 0.48

June 7, 1977 SN 0.35 0.31 0.42 0.42

to June 2, 1978 OT 0.14 0.08 0.15 0.20

Sum 0.49 0.39 0.57 0.62

s h o w th e h ig h e s t v a lu e s. I n m o s t in s ta n c e s 1 /1 ir r ig a te d p lo ts sh o w h ig h e r v a lu e s t h a n 1 /2 ir r ig a te d p lo ts (a s h , N, P , a n d M g ). I t s h o u ld o n ce m o re b e n o te d t h a t o n ly m a r g in a l a tte n tio n c a n be p a id to K -v a lu e s b e c a u s e of th e w a s h in g -o u t o f th is e le m e n t b y th e ra in fa ll.

T h e tu r n - o v e r o f n u tr ie n ts o n a y e a r ly b a s is is as fo llo w s:

N : 45 — 74 k g / h a P : 6 .3 — 11.3 k g / h a ( K) : 14 — 22 k g / h a M g: 3 .9 — 6.2 k g / h a

d. I n c r e m e n t a n d n e e d l e fall.

O n e re a s o n f o r c a r r y in g th r o u g h th is in v e s tig a tio n w a s to e lu c id a te w h e th e r th e tr e a tm e n ts in th e ir r ig a tio n t r ia l h a v e a n y in flu e n c e o n th e n e e d le fa ll. I t m a y be p r e s u m e d t h a t a n y in flu e n c e o n in c r e m e n t re fle c ts tr e a tm e n t- in d u c e d d iffe re n c e s in le a f a r e a in d e x , w h ic h in t u r n r e s u lt in p a r a lle l d iffe re n c e s in n e e d le fall. In F ig u r e 4 n e e d le fa ll v a lu e s ( t / h a ) a re p lo tte d a g a in s t m e a n a n n u a l b a s a l a r e a in c r e m e n t ( m 2/ h a ) in th e 5 -y e a r p e rio d d u r in g w h ic h th e tr e a tm e n ts h a v e so f a r b een c a r r ie d th r o u g h . T h e

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N k g / h a 100

N

g /itv *

o control + - th ro u g h fa ll

*1/2 irrig a te d

#1/1 irrigated --- Spruce needles --- Other things

Total litterfaU

5 0 -

10

days

F i g u r e 3. The cum ulative con ten t of N in litter fall.

F i g u r 3. Det s u mme r e d e N-i ndhol d i st r øfal det ( se i øvr i gt tabeltekster).

(15)

4,00

3,50

3,00

, y e a r

F i g u r e 4. Needle fall p lotted against average basal area in crem en t in the fore­

going 5 y ears’ period.

F i g u r 4. Nål ef al d lagt o p over årlig grundf l ade t i l v æks t i den f orudgående 5 års-periode.

re g re s s io n -lin e is e s tim a te d ; h o w e v e r, th e c o r r e la tio n c o e ffic ie n t r = 0.816 is s ig n ific a n t (0.01 < p < 0 .0 2 ), w h ic h is a s tro n g s u p p o r t o f th e w 'o rk in g h y p o th e s is .

D ISC U SSIO N

A s m e n tio n e d in th e in tr o d u c tio n , th e a u th o r s h a v e f o u n d i t p r e f e r ­ a b le n o t to m a k e a t r a d itio n a l re v ie w of th e lite r a tu r e . In T a b le 10 so m e p u b lis h e d f ig u r e s a re p r e s e n te d to g e th e r w ith a few r e m a r k s a n d w ith th e c o m p a ra b le f ig u r e s f r o m th e p r e s e n t in v e s tig a tio n . T h e r e is o n e r e m a r k to b e m a d e a b o u t th e fig u re s , th e y all com e fro m s ta n d s w ith clo sed c a n o ­ p ies, b u t a p a r t fro m th is th e ir o r ig in s a re d if f e r e n t c o u n tr ie s in E u ro p e , a n d a sin g le N o r th A m e ric a n s ta n d is in c lu d e d , too. A lso, th e s ta n d s h a v e v a ry in g ages, a n d site f a c to r s a s w e ll a s h e ig h t above se a level v a r y a good deal.

T h e fig u re s in th e ta b le v a ry v e r y m u c h . T h e lo w e s t fa ll o f n ee d le s h a s b e e n fo u n d b y B o r n e b u s c h (1 9 3 7 ), th e h ig h e s t b y G l o a g u e n a n d T o u f f e t

i d n e e d l e fal l

4 '9mL

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T a b l e 10. Sum m ary of results from litte r fall studies in N orw ay spruce stands.

T a b e l 1 0 . Samme n f a t ni ng af pu b l i c e r e d e str øfal ds undersøgel ser i rødgran.

k g litte r kg N

R eference p e r h a

a n d y e a r k g s tr ø

% n eed les p e r h a a n d y e a r k g N

R e m a rk s

F o r f a t t e r p r . h a

og å r

% n å l e p r . h a og d r

B e m æ r k n i n g e r

Aussenac, 1969 2924 85.6 1 stand, average of 2

years. Needle fractio n 1 year.

Bonnevie-Svendsen

and Gjems, 1957 2996 75.8 29.0 Average of 4 stands and

2 years. The am ount of litte r seems to be co r­

related w ith stand den­

sity (basal area).

Bornebusch, 1937 1499 _ Average of 3 stands and

2 years, needles only.

C handler, 1943 3767 -- 38.6 1 stand an d 1 year,

needles only.

D ietrich, 1963 3217 79.5 32.0 Average of 4 stands and

2 years.

Duvigneaud et al. 1972 3141 86.4 — 1 stand an d 1 year.

Gloaguen et Touffet,

1976 7369 91.9 68.5 1 stand, average of 4

years.

Gossuin, 1974 2632 83.2 — 1 stand, average of 3

years.

H unger, 1975

Control 2678 74.6 33.2 1 stand \ average of

F ertilized 2746 77.7 35.9 1 stand J 3 years.

Kollist, 1967 3300 Quoted from F o restry

abstracts, 1969.30:597.

L indberg och Nor-

m ing, 1943 3089 — 29.7 1 stand and 1 year,

needles only.

Mork, 1942 2989 81.8 35.5 Best stan d out of 4,

average of 3 years.

N ihlgård, 1972 5720 76.2 58 1 stand average of

3 years.

R ok’yanis, 1974 2328 63.7 13.3 Average of 5 stands,

1 year.

Viro, 1955 2524 72.9 21.2 Average of 3 stands and

4 years.

T he p resen t investigation:

— T hroughfall 3588 83.6 44.9 I

Control 4390 78.0 59.5 1 Average of 2 plots,

1 /2 irrig ated 4926 80.2 63.3 1 1 year.

1/1 irrig ated 5213 75.7 74.1

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(1 9 7 6 ). I n b o th c a se s th e s tu d ie s w e re c o n tin u e d f o r m o r e th a n o n e y e a r ; th e r e f o r e th e r e is h a r d ly a n y re a s o n to believe t h a t th o s e tw o in v e s tig a tio n s r e p r e s e n t a ty p ic a l in s ta n c e s , f o r in s ta n c e d u e to sev ere d ro u g h ts , w h ic h c o u ld c a u s e h e a v y n e e d le fa ll in th e d r o u g h t y e a r a n d d e c re a s e d n e e d le fa ll i n th e fo llo w in g y e a r.

In m o s t o f th e p u b lic a tio n s , e s tim a tio n s o f th e s a m p lin g e r r o r s a re p re s e n te d , a n d th e y sh o w t h a t th e m e th o d s u s e d a re good e n o u g h to w a r ­ r a n t s ig n ific a n t d iffe r e n c e s b e tw e e n th e in v e s tig a tio n s ; h o w e v e r, n o th in g c a n be s a id a b o u t a n y b ia s d u e to th e s a m p lin g m e th o d s u s e d . A b ia s m a y b e e x p e c te d to be n e g a tiv e in th e se n se th a d n e e d le s a n d o th e r th in g s p a s s th r o u g h th e w a te r d r a in s in th e c o lle c tin g d ev ices, le a d in g to lo w e r l itte r fa ll v a lu e s th a n th e tr u e l i t t e r fall. C o n c e rn in g th e p r e s e n t s tu d y , f r e q u e n t in s p e c tio n s o f th e f u n n e ls h a v e m a d e th e p o s s ib ility of lo s in g n e e d le s i n ­

s ig n if ic a n t; h o w e v e r, a lo ss o f m in o r p a r tic le s of o th e r th in g m a y o c c u r.

In th is c o n n e c tio n i t sh o u ld b e n o te d t h a t th e r e la tiv e n e e d le f r a c tio n s of th e to ta l l itte r fa ll, a lth o u g h v a ry in g a m o n g in v e s tig a tio n s a n d w ith in i n ­ v e s tig a tio n s , give n o s u p p o r t f o r a n y h y p o th e s is a b o u t b ia s e d e s tim a te s of o th e r th in g s .

A t th is sta g e o f l itte r fa ll s tu d ie s i t seem s f a ir to s ta te t h a t th e r e a re g r e a t v a r ia tio n s w ith in a re g io n lik e N o r th e r n E u ro p e , w h ic h c a n n o t be e x p la in e d b u t m u s t be ta k e n a s p la in f a c ts . It c a n b e seen fr o m th e f ig u re s i n T a b le 10 th a t th e la te s t D a n is h f in d in g s fa ll w ith in th is v a r ia tio n r a n g e , a lth o u g h , o n a n a v e ra g e , th e y a re s o m e w h a t h ig h e r th a n th e g e n e ra l m e a n .

T a b le 10 also, sh o w s th e N -tu rn o v e r in th o s e s tu d ie s w h e re N -a n a ly se s h a v e b e e n c a r r ie d th r o u g h . T h e D a n is h in v e s tig a tio n s h o w s r e la tiv e ly h ig h a m o u n ts o f N. As to th e D a n is h fin d in g s , th e tr e a tm e n t- in d u c e d d if f e r e n ­ ce s in k g N p e r h a a re m a in ly c a u s e d b y th e d iffe re n c e s in a m o u n t o f l i t ­ te r. I t is w o r th m e n tio n in g , to o , t h a t th e D a n is h s ite is r a t h e r fe rtile .

A s to th e level o f o th e r n u tr ie n ts , th e tu r n o v e r in th e D a n is h s tu d y is a lso h ig h e r t h a n th e fig u re s fro m o th e r s tu d ie s , w h ic h is u n d e r lin in g t h a t th e f e r tility o f th e s ite u n d e r c o n s id e r a tio n is h ig h .

M o r k (1942) c la im s t h a t th e a m o u n t o f l i tte r p e r y e a r is d e p e n d e n t on site q u a lity , age o f s ta n d , a n d h e ig h t ab o v e sea level. 4 o b s e rv a tio n s c a n h a r d ly s u p p o r t th is w id e c o n c lu sio n .

H u n g e r (1975) s ta te s t h a t th e d iffe re n c e b e tw e e n h is 2 p lo ts is close to b e in g s ig n ific a n t (0.05 < P < 0 .1 0 ). H e also d e m o n s tr a te s t h a t th is d if ­ fe re n c e is d u e to a la r g e r l i t t e r fa ll j u s t a f te r th e fe r tilis a tio n .

A p a rt f ro m th o s e tw o re f e re n c e s a n d in c o n tr a d ic tio n to M ø l l e r’s (1 9 4 4 ) c o n c lu s io n s m e n tio n e d in th e in tr o d u c tio n , it is f a ir to s tre s s t h a t th e p r e ­ s e n t s tu d y d e m o n s tr a te s a p o sitiv e c o r re la tio n b e tw e e n in c r e m e n t a n d a m o u n t o f litte r fa ll, w h ic h is n ew a n d in c lo se r a g r e e m e n t w ith c o m m o n se n se e x p e c ta tio n s th a n M ø l l e r ’s s ta te m e n ts a re .

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SUMMARY

In an irrig a tio n tria l in 21-year-old N orw ay sp ru ce on fertile clayey m oraine (Holstener-Jørgensen a n d Hol msgaard, 1977) the am ount of litte r fall w as meas­

u re d and its chem ical com position determ in ed over a p erio d of a year (1977/78).

The tables an d figures of the re p o rt show the follow ing —

The am ount an d chem ical com position of the litte r fall are d ep en d en t on th e treatm ents ap p lied in the trial. In screened-off plots w h ere p a rt of th e sum ­

m er p re c ip ita tio n is diverted, the litte r fall is th e poorest, 3.6 tons p e r ha, of w h ic h 3.0 tons are needles. The am ounts are in creasin g w ith the im provem ent of the w a te r supply to the plots. In 1/1 irrig a te d plots the litte r fall is 5.2 tons p e r ha, of w h ic h 3.9 tons are needles.

W ith the litter, p la n t n u trien ts are retu rn e d to th e soil. T hus, in screened-off plots 44.9 kg N p e r h a is retu rn e d , in fully irrig a te d plots 74.1 kg p e r ha.

Møll er (1944) on the basis of his studies in closed stands concluded th a t the am ount of needles is in d ep e n d en t of —

(1) age of stand (2) heig h t of stan d (3) site quality

(4) grade of th in n in g w hen m easured a couple of years afte r the last th in ­ ning.

In the irrig a tio n trial, w h ic h is un th in n ed an d has fully closed canopy, there is a correlation betw een needle fall and basal a re a increm ent (Figure 4 ), w hich is in closer agreem ent w ith com m on sense than M øller’s conclusions are.

DANSK SAMMENFATNING

I et vandingsforsøg i 21-årig rø d g ran på fru g tb a r lerm oræ ne (Hol s t ener- Jørgensen an d Hol msgaard, 1977) er strøfaldets størrelse m ålt og dets kem iske sam m ensæ tning bestem t over en p erio d e p å et å r (1977/78).

B eretningens tab eller og fig u rer v iser følgende:

Strøfaldets stø rrelse og kem iske sam m ensæ tning er afhæ ngige af forsøgets behandlinger. I skæ rm ede p arceller, h v o r en del af som m ernedbøren ledes bort, e r strøfaldet m indst, nem lig 3.6 t p r. ha, hvoraf 3.0 t er nåle. M ængderne stiger m ed fo rb ed rin g af p a rcellern es vandforsyning. I 1/1 vandede p arc e lle r er strø­

faldet 5.2 t p r. ha, h v o raf 3.9 t er nåle.

Med strø et re tu rn e re s p lantenæ ringsstoffer til jorden. I skæ rm ede p a rceller retu rn e res således 44.9 kg N p r. ha, i fu ld t vandede 74.1 kg N p r. ha.

Møller (1944) konkluderede p å grundlag af sine stu d ier i sluttede bevoks­

ninger, at nålem æ ngden er uafhæ ngig af 1) bevoksningsalder

2) bevoksningshøjde 3) b onitet

4) ty ndingsstyrke ved undersøgelse et p a r å r efter sidste tynding.

I vandingsforsøgets behandlingsled, hvor bevoksningerne er fu ld t sluttede og utyndede, er d e r en k o rrelatio n mellem nålefald og grundfladetilvæ kst (figur 4), som e r i bedre overensstem m else m ed sund fo rn u ft end Møllers konklusioner.

Oxford Classific. No. 114.351, 160.21, 561.25 Picea abies.

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REFERENCES

Aussenac, G., 1969: P ro d u c tio n de litiére dans divers peuplem ents forestiers de l ’est de la F rance. Oecol. P lant. 4: 225— 236.

Bonnevi e- Svendsen, C., a n d 0 . Gjems, 1957: Amount an d chem ical com position of the litte r from larc h , beech, N orw ay spruce and Scots p in e stands and in effect on the soil. Medd. Norske Skogforsøksv. 14: 111— 174.

Bornebusch, C. H., 1937: Iagttagelser over R ødgranens N aalefald. Forsti. Forsøgsv.

Danm. 14: 173— 176.

Chandler, R. F., 1943: A m ount an d m in eral n u trie n t content of freshly fallen needle litte r of some n o rth ea stern conifers. P roc. Soil Sei. Soc. Amer. 8:

409— 411.

Di et rich, H., 1963: U ntersuchungen zum N ährstoffkreislauf von F ich tenbeständen im Osterzgebirge. Arch, fü r F orstw . 12: 1116— 1136.

Duvigneaud, P., E. Paulet, P. Ke st e mont , M. Tanghe, S. Denaey er- de Smet, G. S c h n o c k et J. Ti mp e r ma n , 1972: P ro d u ctiv ité com parée d’une hétraie (Fagetum ) et d’une pessiére (P iceetum ), établies sur méme rochem ére, å M irw art (A rdenne Luxem bourgeoise). Bull. Soc. roy. Bot. Belg. 105: 183—■

195. '■

Gloaguen, J. C. et I. Touffet, 1976: P ro d u ctio n de litié re et ap p o rt au sol d’élé- m ents m in érau x dans quelques peuplem ents résineux de Bretagne. Ann.

Sei. forest. 33: 87— 107.

Gossuin, A., 1974: P ro d u ctio n de litié re dans une hétraie et une pessiére de H aute- A rdenne. Bull. Soc. roy. Bot. Belg. 107: 9— 22.

Holstener-Jørgensen, H. a n d E. Hol msgaard, 1975: F ertilizatio n and irrig a tio n of young N orw ay sp ru ce on sandy soil. Forsti. Forsøgsv. Danm. 34: 263— 270.

Holstener-Jørgensen, H. og V. Johansen, 1975: V anding af nobilis-klippebevoks- ninger. Forsti. Forsøgsv. Damn. 34: 307— 316.

Holstener-Jørgensen, H. a n d E. Hol msgaard, 1977: The dependence of the in c re ­ m ent on the w a te r supply in a young N orw ay spruce stand. F orsti. F o r­

søgsv. Danm. 35: I I — 14.

Hunger, W., 1975: Streum enge u n d S treuqualität im älteren F ich ten b estan d u n te r n atü rlich en und k ünstlichen v erän d erten E rnähru n g sv erh ältn issen . F lora, 164: 449— 478.

Li ndberg, S. och H. Normi ng, 1943: Om p ro d u k tio n en av b a rrfö rn a och dennas sam m ensättning i ett granbestånd invid Stockholm. Svenska Skogsvårds- fören. T. 41: 353— 360.

Madgwi ck, H. A. J. a n d J. D. Ovington, 1959: The chem ical com position of p r e ­ c ip itatio n in adjacent forest and open plots. F o re stry 32: 14— 22.

Madsen, T. L., P. Moltesen og P. O. Olesen, 1978: T yndingsstyrkens indflydelse p å rødgranens rum tæ thed, tørsto fp ro d u k tio n , grentykkelse og grenm ængde.

Forsti. Forsøgsv. Danm. 36: 181— 203.

Mork, E., 1942: Om strøfallet i våre skoger. Medd. norske Skogsforsøksv. no. 29:

297— 365.

Møller, C.Mar: 1944: U ntersuchungen üb er Laubmenge, Stoffverlust und Stoff­

pro d u k tio n des W aldes. F orsti. Forsøgsv. Danm. 17: 1— 287.

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Nihlgård, B., 1972: P la n t biom ass, p rim a ry p ro d u ctio n an d d istrib u tio n of che­

m ical elem ents in a beech an d a p lan ted sp ru ce forest in South Sweden.

Oikos, 23: 69— 81.

R o k ’yanis, B., 1974: (Seasonal litte r fall an d its role in the biological cycle of m aterials in spruce stands of the V accinium type on h illy m oraines) Lat- vijas L auksaim niecibas A kadém ijas R aksti no. 75: 27— 37.

Tamm, C. 0. , 1951: Rem oval of p la n t n u trien ts from tre e crow ns by rain. Physiol.

P lan taru m 4: 184— 188.

Viro, P. J., 1955: Investigations on forest litter. Conimun. Inst. for. Finl. 45: 1-—65.

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R e t t e l s e til n r . 282. H. C. O ls e n : V e d m a s s e ta b e l fo r rø d g r a n i D a n m a r k . B in d XXXIV.

D a fo rm le rn e ( 1 3 ) , (1 4 ) og (1 5 ) v ed e n b e k la g e lig fe jl er a n f ø r t u d e n k o r r e k tio n s v a re n d e til, a t d m å le s i cm , b e d e s fø l­

g e n d e r e tte ls e r fo r e ta g e t:

sid e 380: i (1 3 ) r e tte s „— 2 log d “ til „— 2 log ( d / 1 0 0 ) “ s id e 381: i (1 4 ) r e tte s „0.000977“ til „4.000977“

sid e 381: i (1 5 ) r e tte s „ 0 .105887“ til „4.105887“

Referencer

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