WORKING PLAN OF DEHRA FOREST DIVISION FOR THE PERIOD …hpforest.nic.in/files/Dehra Vol-1 part...
Transcript of WORKING PLAN OF DEHRA FOREST DIVISION FOR THE PERIOD …hpforest.nic.in/files/Dehra Vol-1 part...
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WORKING PLAN OF DEHRA FOREST DIVISION
FOR THE PERIOD OF
2012- 2013 to 2021-2022
VOLUME-1 (PART-I & PART-II)
BY
G.R. SAHIBI, IFS
Conservator of Forests cum WPO Dehra
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CONTENTS
Subject Paragraph
Page
P a r t - 1
S U M M A R Y O F F A C T S O N W H I C H T H E P R O P O S A L S A R E B A S E D
C H A P T E R - I
T H E T R A C T D E A L T W I T H
Nam e and s i tuat io n 1 2
Conf igu rat ion of g round 1 .2 2
Geo log y, rock and so i l 1 .3 2
Upp er Sh iva l iks 1 .3 .2 2
P in jo r B ou ld e rs Bed 1 .3 .3 2
Geo log y of D eh ra 1 .3 .4 2
So i l and Fore st D is tr ibut io n 1 .4 3
C l im ate 1 .5 3
Ra in Da ta T ab le- 1 3
So me ra in fa l l data of Dha ram sa la T ab le- 2 4
Te mpe ra tur e/Hu m id i ty T ab le -3 4 -5
Wa t er supp ly 1 .6 5
D is t r ibu t ion of a r ea 1 .7 5-6
Ar ea Stat em ent T ab le-4 6
S ta t em en t of s e i sm ic in fo rm at io n T ab le-5 6
St at e of bounda r ies ta b le-6 7
Expend itur e on Bou nda r y P i l la rs T ab le-6 7
Lega l po s i t ion 1 .9 8
Ba rn e’s Land Re venue Se tt leme nt (1 849-185 2) 1 .9 .1 8
BanMuaf i and unc la sse d For est s 1 .9 .2 8
Lya l l ’ s Re v ised Land Re venu e Se tt l em en t 1 .9 .3 8-9
(1 865-1 86 9)
Sc hem e of Ro e and Duf f (1 872 -1875 ) 1 .9 .4 9
And e rson ’s Fo r est Se tt l em en t (1883-18 87 ) 1 .9 .5 9 -10
Sp e c ie s U/S 3 0 (a ) IFA T ab le-7 10- 11
G ibson S Fo re st se tt l em en t 1 .9 .6 12
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Mi dd le t ion ’s R e v ise d La nd R evenue Se t t lem en t 1 .9 .7 12
Mi tch e l l a nd Wa lte r ’ s Ro tat iona l C lo su re Sc heme 1 .9 .8 1 2-1 3
Su mma r y of the Re su lt s o f the Se tt le ment and 1 .9 .9 14
Sc hem es
The Co- opp erat i ve For es t Soc iet ie s : 1 .1 0 14
Act ive JFM C s i n De h ra T ab le 8 14
Not e on abol i t io n o f Pa ym ent of haq -ch uha ram 1 .1 0.1 15
The Himacha l P rad e sh comm on land Act 1974 1 .1 1 15
The Fore st Con se rvat io n A ct , 1980 1 .1 2 15
Lega l Po s it ion 1 .1 3 15
R igh ts & conce ss io ns 1 .13 .2 15
R igh ts in re ser ve d f o re st s 1 .1 3.4 16
R igh ts in pr o te cted fo re st s 1 .1 3.5 16
R igh ts in un- c lass ed fo re st s 1 .1 3.6 16
Su mma r y of pr inc ipa l r igh t s 1 .1 4 17
T .D . R igh t s in De h ra D i v is ion 1 .1 4.1 17-1 8
Pr ese nt P os it i on 1 .1 4.2 1 8-1 9
Ba ck in g u p of la nd f or cu lt ivat ion 1 .1 4.3 19
T i mbe r f or bu i ld ing purpose 1 1 .4 .4 19-2 0
Rate s T ab le-9 20
Fr o m DP F T ab le-10 2 0-2 3
T i mbe r and wood fo r bu rn ing the d ead, fu ne ra l 1 .14.5 24
and ma rr iag e ce re moni es , ag r icu l tu ra l impl eme nts
Gran t f o r marr iag e and fun e ra l e t c Tab l e-1 1 25
Gra z ing 1 .1 4.6 2 6
Gadd i Graz ing 1 .1 4.6 .1 26
Lopp ing 1 .1 4.7 26-2 7
Z im in dar i sha re s 1 .1 4.8 27
Su r vey and De ma rca t io n 1 .1 5 27
Cons t i tu t ion of D PF 1 .1 6 27
C H A P T E R – I I
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FLO RA AND FA UNA
T h e F o r e s t F l o r a 2 A 2 8
Com po s i t ion and d is tr i bu t ion of Fo res t 2 .1 28
Mi sce l laneou s Scr ub Fo re sts 2 .2 28
Typ e 5 B/C 2 M ixed Dec iduo us Fore st s 2 .2 1 28-2 9
Tr e es 2 .2 .2 29
Sh rubs 2 .2 .3 29
Gra ss es 2 .2 .4 29
C l im be rs 2 .2 .5 29
Typ e 5 B/D SI D ry De c iduous scrub 2 .2 .3 29
Typ e 9 Cla L ow er Sh iwa l ik Ch i l P ine Fo re st s 2 .4 29-3 0
Typ e 5 B/E 9 D r y Bam bo o brakes 2 .5 30
F l or i s t ic 2 .5 .1 30-3 1
Are a co ve red und er Fo re st t ype T ab le-12 3 1
Gene ra l d escr ip t ion of g row ing st ock 2 .6 31
In ju r i es t o wh ich crop i s l iab le 2 .7 31
F i re 2 .7 .1 31-3 2
Rang e w ise Fo res t f i re repor t T ab le-13 32- 33
Fau l t y Res in Tapp ing and con sequen ce s 2 .8 3 4
B la zes T ab le-13 A 3 4
C l im ate 2 .9 35
C l im ate Chang e 2 .9 .1 35
D rough t 2 .1 35
Er os ion 2 .1 1 35
Wind 2 .1 2 35
Lopp ing 2 .1 3 35-3 6
I l l i c i t Lopp ing T ab le-13 B 36
Gra ss cu tt ing 2 .1 4 36
Ma r k ing and Fe l l ing 2 .1 5 36
Insect s and Fung i 2 .1 6 36-3 7
C l im be rs 2 .1 7 37
Al ie n Inva s ive Spe c ies 2 .1 8 37
La ntana a sse ssm en t Su r vey T ab le-14 37
Gra z ing 2 .1 9 37
Ca tt le cen su s T ab le- 15 37
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Gra z ing P e rm it s T ab le-16 38
En croa chm ents 2 .2 0 38
En croa chm ent Ca ses T ab le -17 38
Bounda r y P i l la r s T ab le 18 39
Human Le opa rd Conf l i c t Ca se s T ab le 19 39
Mon key P rob lem Area s 2 .2 0.2 39-4 0
App r ox im at e Numbe r of Monkey T ab le-20 40
D eta i l s of V u l tu re n est ing s it es 2 .2 0.3 40
Pong W e t Land Map 2 .2 0.3 41
C H A P T E R - I I I
U T I L I Z A T I O N O F T H E P R O D U C E
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Human Popula t io n 3 .1 42-4 3
Ma r ket & m ar ketab le- prod ucts 3 .2 43
Re s in 3 .2 .1 43
Bamb oo 3 .2 .2 43
D eta i l s of Bam boo and res in e xtra ct ion T ab le 22 43
Ch i l T imb e r an d Pu lpwood 3 .2 .3 43
Katha 3 .2 .4 43
Katha E xpor t T ab le-23 44
F i re w ood and Cha rc oa l 3 .2 .5 44
L ine of E xpor t 3 .3 44
Pa st and cur ren t pr ice s 3 .4 44
Co st of va r ious For e st produ cts o f Fat ehpur D iv T ab le-24 44
Co st of va r ious For e st produ cts o fHam i rpur D i v T ab le-25 45
C H A P T E R - I V
A C T I V I T I E S O F H . P . S T A T E F O R E S T D E V . C O R P O R A T I O N
H a r v e s t i n g a n d M a r k e t i n g o f F o r e s t P r o d u c e 4 . 1 4 6
A n u n d e r t a k i n g o f H P G o v t . 4 . 1 . 1 4 6
7
T h e O b j e c t i v e s o f C o r p o r a t i o n 4 . 1 . 2 4 6
E x p e r t i s e o f C o r p o r a t i o n 4 . 1 . 3 4 6
R e s i n P r o c e s s i n g 4 . 1 . 4 4 6
A w a r d i n g T e n d e r s 4 . 1 . 5 4 6
J u r s i d i c t i o n o f F o r e s t W o r k i n g D i v i s i o n s 4 . 1 . 6 4 6
C h i l G o v t . L o t W o r k e d i n F a t e h p u r F o r e s t T a b l e — 2 6 4 7
W o r k i n g D i v i s i o n
C h i l P v t . L o t W o r k e d i n F a t e h p u r F o r e s t T a b l e - 2 7 4 7
W o r k i n g D i v i s i o n
L o t s w o r k e d i n D e h r a F D u n d e r F C A t h r o u g h
F a t e h p u r F W D T a b l e - 2 8 4 7
R e s i n E x t r a c t e d f r o m D e h r a F D a n d d i s p a t c h e d
T o R & T B i l a s p u r T a b l e - 2 9 4 8
G o v t . L o t W o r k e d i n D e h r a F D t h r o u g h F W D T a b l e - 3 0 4 8
H a m i r p u r
P v t . . L o t W o r k e d i n D e h r a F D t h r o u g h F W D T a b l e - 3 1 4 8
H a m i r p u r
G o v t . C h i l L o t W o r k e d i n D e h r a F D t h r o u g h F W D T a b l e - 3 2 4 9
F a t e h p u r
P v t . C h i l L o t W o r k e d i n D e h r a F D t h r o u g h F W D T a b l e - 3 3 4 9
D e t a i l s F C A r e m o v a l s t h r o u g h F a t e h p u r F W D T a b l e - 3 4 4 9
B a m b o o l o t s w o r k e d i n D e h r a F D t h r o u g h F W D
F a t e h p u r T a b l e - 3 5 5 0
R e s i n T A P P I N G 4 . 3 5 0
R i l l M e t h o d 4 . 3 . 1 5 0
F r e s h e n i n g 4 . 3 . 2 5 0 - 5 1
A p p l i c a t i o n o f s t i m u l a n t 4 . 3 . 3 5 1
T a p p i n g S e a s o n 4 . 3 . 4 5 1
U s e o f g u i d e 4 . 3 . 5 5 1
I n s t a l l a t i o n d u r i n g S u b s e q u e n t y e a r s 4 . 3 . 6 5 1
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C H A P T E R – V
F O R E S T R Y U N D E R V A R I O U S F I V E Y E A R S P L A N
Gene ra l 5 .1 52
1s t
F ive Y ea r P lan T ab le- 36 52
I i nd F i ve Yea r P lan Tab le-3 7 5 2-5 3
I I I rd F ive Y ea r P lan T ab le - 38 53
IVt h F i ve Yea r P lan T ab le- 39 53
Vt h F ive Y ea r P lan T ab le- 40( A) 54
VI t h F ive Yea r P lan T ab le- 40( B ) 54
VI I t h F ive Y ea r P lan T ab le- 40( C ) 54-5 5
VI I I t h F ive Y ea r P lan T ab le- 40( D) 55
IXt h F ive Year P lan T ab le- 40( E ) 55-5 6
X th F ive Y ear P lan T ab le- 40( F) 56
X I th F ive Y ea r P lan T ab le- 40( G) 56
C H A P T E R - V I
S T A F F A N D L A B O U R S U P P L Y
St a f f 6 .1 57
Po s it ion of Sta ff A S ON 0 1-0 1-2 012 T ab le- 41 57
La bour Supp ly 6 .2 57
Da i ly Wage r s ra tes chang es T ab le 42 58
C H A P T E R - V I I
P A S T S Y S T E M O F M A N A G E M E N T
Ea r ly h is tor y of Gu l er Sta te 7 .1 59-6 1
S i ba State 7 .2 61-6 2
D eh ra fo r ests in the pas t 7 .3 62-6 3
Gene ra l H is tor y of the Fore st s 7 .4 63
Pa st sy stem s o f manag em ent and th ei r r esu l ts 7 .8 64
The pe r iod of o rgan i za t ion 7 .8 .1 65
The pe r iod of t ran s i t io n 7 .8 .2 65
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The pe r iod of sc i ent i f i c manag eme nt 7 .8 .3 66
Her t z Wor k ing P lan 7 .8 .4 66
P ine W ork ing C i r c le 7 .9 .1 66
Sc rub Wo rk i ng C i r c le 7 .9 .2 66
The Oak Wo r k ing C i rc le 7 .9 .3 66
Re su l ts 7 .9 .5 66
The sch eme of ro ta t iona l c losur es 7 .1 0 66-6 7
by M itch el l and Wa lter s
Wa it e r 's W or k ing P lan 7 .1 1 67
Kangra P in e Wo rk ing C i r c le 7 .1 1.1 67
The Oak Wo r k ing C i rc le 7 .1 1.2 68
D eo dar and F i r W o rk ing C i rc le 7 .1 1.3 68
T he Coppi ce Wor k ing C i r c le 7 .1 1.4 68
The Unwo rkab le Wo rk ing C i rc le 7 .1 1.5 68
Mohan 's Wo rk ing P lan (193 3-3 4 to 195 0-51) 7 .1 2 68
The Ch i l She l te rwoo d wo rk ing c i rc le 7 .1 2.1 68-6 9
The Oak She l te rwood wo r king c i rc l e 7 .1 2.2 69
The Co ppice Wo rk i ng C i r c le 7 .1 2.3 69-7 0
The Se lect ion Wor k ing C i r c le 7 .1 2.4 70
The Pro te ct ion W o rk ing C i rc le 7 .1 2.5 70
Su mma r y of Mohan ’s P lan 7 .1 2.6 70
Re vised Wor k ing P lan of Rom e sh 1950-51 7 .1 3 70
Re vised Wor k ing P lan of Malhotra ’s 7 .1 4-7 .29 72-8 2
Re wa ls In teg ra te d Wo rk ing P la n 7 .3 0-7 .34 82-9 6
MP S ingh P lan (1 98 1-82 t o 7 .3 5 96-9 8
199 5-9 6 )
Ba ld ev S ingh s F i f th Wo r k ing P la n 7 .3 5.1 98
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C H A P T E R - V I I I
S T A T I S T I C S O F G R O W T H A N D Y I E L D
Gene ra l 8
Vo l ume tab l e fo r th e r ight ban k 8 Tab le4 9 99
Vo l ume Tab le f or va r ious h e ight c las se s 8 .1 Tab le 50 99
Vo l ume tab l e fo r th e le f t ban k 8 .2 Tab le 51 99-1 00
D ia me ter Ag e Re la t ionsh ip 8 .3 Tab le52 100
Vo l ume In cr em ent tab le for the 8 .4 Tab le 53( A) 100- 10 1
r igh t ban k f e l l ing se r ie s
Vo lum e Incre ment tab l e fo r th e 8 .4 . 1 Tab le 53( B )
101
Lef t bank f e l l ing se r ie s
Vo l ume Tab le f or M ixe d B.L . Spe c ie s 8 .5 Tab le 5 4 101
Fu e l w ood 8 .6 101
St o ck ing pe r he cta re c lass i f i cat ion T ab le 55 102
Kha i r 8 .7 Ta b le 56- 59 10 2 103
Ann ual m o rta l i t y ra t e 8 .8 104
Vo l ume and we ig ht T ab le 60 104
So me con ver s ion fac to rs 8 .9 104
Char coa l 8 .9 . 1 104
Qua l i t y c las se s 8 .10 1 04
D en s i t y 8 .11 10 4
St o ck Maps 8 .12 10 4
Enum era t ion 8 .13 1 05
Re gen e ra t ion Su r vey 8 .14 1 04- 105
Sa l 8 .14 .1 Table 60 (A ) 105
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C H A P T E R - I X
E S T I M A T E O F C A P I T A L V A L U E O F F O R E S T S
Gro wing Stock Est i mate s 9 106
La nd 9 .1 106
Gro wing Stocks 9 .2 106
C H A P T E R - I
B A S I S O F P R O P O S A L
Gene ra l ob je cts o f m anag em ent 1 1 07
C h i l S h e l t e r w o o d W o r k i n g C i r c l e 1 . 2 1 0 7
C o p p i c e W o r k i n g C i r c l e 1 . 2 . 1 1 0 8
T h e B a m b o o R e - h a b i l i t a t i o n W o r k i n g C i r c l e 1 . 3 1 0 8
T h e P r o t e c t i o n - c u m - R e h a b i l i t a t i o n
W o r k i n g C i r c l e 1 . 4 1 0 8
K h a i r ( o v e r l a p p i n g ) w o r k i n g c i r c l e 1 . 5 1 0 8
P l a n t a t i o n W o r k i n g C i r c l e 1 . 6 1 0 8
W i l d L i f e W o r k i n g C i r c l e 1 . 7 1 0 8
J o i n t F o r e s t P l a n n i n g & M a n a g e m e n t
W o r k i n g C i r c l e 1 . 8 1 0 9
N T F P W o r k i n g C i r c l e 1 . 8 . 1 1 0 9
A r e a c o v e r e d b y d i f f e r e n t s p e c i e s 1 . 9 1 0 9
P e r c e n t a g e o f a r e a c o v e r e d b y d i f f e r e n t
s p e c i e s T a b l e - 6 1 1 0 9
F e l l i n g s e r i e s 1 . 1 0 1 1 0
B l o c k s a n d C o m p a r t m e n t s 1 . 1 1 1 1 0
N o m e n c l a t u r e 1 . 1 2 1 1 0
S o i l S u r v e y 1 . 1 3 1 1 0
T h e P e r i o d o f P l a n 1 . 1 4 1 1 1
A r e a S t a t e m e n t W o r k i n g C i r c l e W i s e T a b l e - 6 2 1 1 2
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C H A P T E R - I I
C H I L S H E L T E R W O O D W O R K I N G C I R C L E
G e n e r a l C o n s t i t u t i o n a n d C h a r a c t e r o f
V e g e t a t i o n 2 . 1 1 1 3
Sp e c ia l ob je cts of m anag em en t 2 .3 1 13
Are a and a l l otm ent 2 .4 1 14
Felling Series T a b l e - 6 3 - 6 7 1 1 4
A n a l y s i s a n d v a l u a t i o n o f t h e c r o p 2 . 5 1 1 5
R . B . f e l l i n g s e r i e s T a b l e 6 8 - 7 2 1 1 5 - 1 1 7
A r e a c o v e r e d b y d i f f e r e n t c l a s s o f F o r e s t i n L e f t B a n k F e l l i n g s e r i e s
1 & 1 1 T a b l e - 7 3 - 7 7 1 1 7 - 1 1 8
S i lv icu l tura l sys tem 2 .7 1 19
C h o i c e o f s p e c i e s 2 . 8 1 1 9
R o t a t i o n a n d C o n v e r s i o n P e r i o d 2 .9 1 19
R e g e n e r a t i o n P e r i o d 2 .1 0 1 20
R e d u c i n g F a c t o r a n d R e d u c e d A r e a 2 .1 1 1 20
D iv is i on in to p e r iods & a l lotm en t to pe r iod ic b loc k 2 .12 1 20
Ca lcu lat ion of y ie ld 2 .1 3 1 20
Cont ro l o f y ie ld 2 .1 5 1 22
Sub s id iary s i lv i cu l tu ra l op erat i on s in P .B . a rea s 2 .1 6 1 23
C H A P T E R - I I I
C O P P I C E W O R K I N G C I R C L E
Gene ra l con st it ut ion and cha racte r o f Vegeta t ion 3 .1 1 25
B lo cks an d com pa rtme nt 3 .2 1 25
Sp e c ia l ob je cts of m anag em en t 3 .3 1 25
Are a and a l l otm ent 3 .4 1 25
Ana lys i s and va luat ion of c rop 3 .5 1 25
Kha i r En umera t ion Tab le- 86 1 26
S i lv icu l tura l sys tem 3 .6 1 25
Ro tat ion , e xp lo i tab le- d iam et e r & r egene ra t ion
pe r iod 3 .7 1 26
Ca lcu lat ion of y ie ld 3 .8 1 26
Se quen ce of fe l l ing Tab le -87 12 7-132
P lan t ing of p rog ramme 3 .9 1 33
Sub s id iary s i lv i cu l tu ra l op erat i on s 3 .1 0 1 33
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C H A P T E R – I V
T H E P L A N T A T I O N W O R K I N G C I R C L E
Gene ra l con st it ut ion and chara cter o f vegeta t ion 4 .1 .1 1 34
B lo cks an d com pa rtme nt 4 .1 .2 1 34
P l a n t a t i o n S e r i e s 4 . 1 . 3 1 3 4
Sp e c ia l ob je cts of m anag em en t 4 .2 1 34
Are a & Al lotm ent 4 .3 1 34
Ana lys i s and va luat ion and crop 4 .4 1 35
Kha i r En umera t ion Tab l e-8 9 1 35
Ch i l Enum e rat ion Tab l e-9 0 1 35
S i lv icu l tura l sys tem 4 .5 1 35
Choic e of Spec ie s 4 .6 1 35
Ro tat ion and Conve r sio n Pe r iod 4 .7 1 35
Ca lcu lat ion of y ie ld 4 .8 1 36
Me thod of exe cu t ing f e l l ing 4 .9 1 36
Se quen ce of Fe l l ing 4 .1 0 1 36
S e q u e n c e o f F e l l i n g Tab le- 91 1 36
Se quen ce of P lan t ing T ab le 92 1 36
Sub s id iary s i lv i cu l tu ra l op erat i on s 4 .1 3 1 38- 139
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C H A P T E R – V
T H E P R O T E C T I O N C U M R E H A B I L I T A T I O N W O R K I N G C I R C L E
Gene ra l p r es cr ipt io n 5 .1 .2 1 40
B lo ck an d C ompa r tm en ts 5 .1 .3 1 40
Sp e c ia l ob je ct of managem ent 5 .2 1 40
Are a and a l l otm ent 5 .2 .1 1 41
Are a and a l l otm ent Tab l e- 9 4 14 1
Ana lys i s and va luat ion of c rop 5 .3 1 41
Ch i l Enum e rat ion Tab le- 95 1 41
Kha i r enu mera t ion Tab l e96 - 97 1 41
B.L . enum era t ion Tab le-98 1 42
S i lv icu l tura l sys tem 5 .5 1 42
Pr ot e ct i on f rom F i r e 5 .1 0 1 42
So i l and Wat e r con ser vat io n 5 .1 1 1 44
Invas i ve A l ien Spe c ies 5 .12 1 45- 150
C H A P T E R – V I
K H A I R ( O V E R L A P P I N G )
W O R K I N G C I R C L E
Gene ra l con st it ut ion and cha racte r o f veget at ion 6 .1 1 51
Sp e c ia l ob je cts of m anag em en t 6 .2 1 51
Ana lys i s and va luat ion of c rop 6 .3 1 51
Kha i r enu mera t ion of fe l l ing s e r ies I & I I T ab le- 102-1 05 1 51- 152
Si lv icu l tura l Syst em 6 .3 .2 1 52
Exp lo i tat ion D iam e ter 6 .3 .3 1 52
Fe l l ing C i r c le 6 .3 .4 1 52
Ca lcu lat ion of Y ie ld 6 .4 1 52
Y i e ld s tat em en t T ab le- 106 1 52
Se quen ce of Fe l l ing T ab le- 10 6 (a) 1 54- 159
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C H A P T E R – V I I
B A M B O O C U M R E H A B L I T A T I O N W O R K I N G C I R C L E
Gene ra l 7 .1 1 60
B lo cks & C ompa r tm ent s 7 .2 1 60
Sp e c ia l Ob je ct s o f Manag em en t 7 .3 1 60
Are a Sta te men t 7 .4 1 60
D ist r ibu t ion of a r ea 7 .5 1 6
Rang e w ise and Fore st wise d i s t r ibut io n of a rea Tab le 108 16 0
Enum era t ion 7 .6 1 61
Ana lys i s & Va lua t ion of C rop 7 .7 1 61
S i lv icu l tura l Syst em 7 .8 1 61
Ro tat ion 7 .9 1 61
Fe l l ing C yc le 7 .1 0 1 61
Ca lcu lat ion of y ie ld 7 .1 1 1 61
Se quen ce of Fe l l ing 7 .1 2 1 61
Se quen ce of Fe l l ing T ab le- 109 1 61
Me thod s of Execut ing Fe l l ing 7 .1 3 1 61
Sub s id iary S i lv icu l tura l Opera t ion 7 .1 4 1 62
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C H A P T E R - V I I I
W I L D L I F E M A N A G E M E N T ( O V E R L A P P I N G ) W O R K I N G C I R C L E
Gene ra l Cons t i tut ion 8 .1 1 63
Ob je ct ive Of Managem en t 8 .2 1 63
Human W i ld L i f e conf l i c t Managemen t 8 .3 .1 1 63
Human /L eopard conf l i c t ca ses 1 10 1 63
Wi l d L i fe C ompen sat ion T ab le-11 1 164
Mon keys Tab le- 112 164
Wi l d B oa r 8 .3 .2 .1 1 65
Vu l tu re C onser vat ion 8 .4 1 65
Vu l tu re ne st ing s i t e 1 13 1 65
L i s t Of M ig rat or y And Loca l B i rd s Tab le- 115 1 66- 167
St r engt hen i ng th e Adm in i st ra t ive Setup 8 .2 1 68
An ima l Hea l th Ca re 8 .3 1 69
Pub l ic Awa ren e ss 8 .4 1 69
Pub l ic it y 8 .5 1 69
Organ iz ing Edu ca t iona l T ou r s & Vi s it s & Compe t it i on 8 .6 1 69
Sh rubs & T r ee s 8 .7 1 70
Ad jo in ing Cat chm ent Ar e a, Khad and Na l la s
D ra in ing Into Pon g Dam 8 .8 1 70
T ab le- 116 1 70
Se quen ce of Wo rks requ i red to be done 8 .9 1 70
So i l Co nser va t ion Wor ks 8 .1 0 1 71
Wa t ch ing To we r s 8 .1 1 1 71- 172
Enfor c ing P ro v is io n of W i ld L i fe P r ot e ct ion Act 1 972 8 .12 172
Re g is t ra t ion of Guns 8 .1 2.1 1 72
Re st r ic t ion on entr y 8 .1 2.2 1 72
Va cc inat i on 8 .1 2.3 1 72
Rat i ona l i za t ion of P rot ecte d ar ea s 8 .1 2.4 1 72
Co l la r ing and sa te l l i te t rack ing s tud ie s of
m ig ra tor y b i rd s in Pong Da m 8 .1 2.5 1 72
17
CHAPTER - IX
JOINT FOREST MANAGEMENT
( O V E R L A P P I N G ) W O R K I N G C I R C L E
J o i n t F o r e s t M a n a g e m e n t i n H . P 9 . 1 1 7 3 - 1 7 4
Ob je ct ive s 9 .4 1 76
JFM Cs in Deh ra Tab le 1 18 17 8-179
P lan ta t ion done in J FM C s in D eh ra Tab le 11 9 1 80- 183
CHAPTER – X
NON TIMBER FOREST PRODUCE(OVERLAPPING)WORKING CIRCLE
General const itution 10.1 184
Specia l objects of management 10.2 184
Blocks and compartments 10.3 184
Area statement 10.4 184
Analysis and evaluation of the crop Table 120 184-185
Stock Maps 10.6 185
Rotat ional extract ion 10.8 185
Forest species of Tropical Himalaya in Trade Table 121 187
18
CHAPTER - XI
MISCELLANEOUS REGULATION
Patty Fel l ing 11.1 188
Deviat ion 11.2 188
Repair of exist ing Roads and Paths 11.4 188
New Build ings 11.5 188
Water Supply 11.7 188
Drought 11.8 188
Maintenance of Boundary Pil lars 11.9 188-189
Quinquenia l Programme for cheking and Maintenance of
Boundary Pil lars Table122 189
Maintenance of Revenue Maps 11.10 190
Rights and concession 11.11 190
Maps 11.13 190
Lopping 11.14 190
I l l ic it Lopping in last f if teen years Table 11.15 190
C H A P T E R - X I I
E S T A B L I S H E D A N D L A B O U R
L is t o f D FO s in D eh ra D i v is ion 1 2 .1 1 92
St a f f 1 2 .2 1 92
D em ar ca t ion Sta ff 1 2 ,2 , 1 1 92
Fo r es t Wo rke r s 1 2 .2 .2 1 93
La bour supp ly 1 2 .2 .3 1 93
The Ro l l of C BOs/ NGO s/SHGs 1 2 .2 .4 1 93
C H A P T E R - X I I I
C O N T R O L A N D R E C O R D S
Com par tm en t h i st or y f i le s 1 3 .1 1 94- 195
Cont ro l fo rm s an d Devi at io n s tatem ent 1 3 .2 1 95
P lan ta t ion journa ls 1 3 .3 1 95
Nur se ry J ourna l s 1 3 .4 1 95
Bounda r y P i l la r s Reg is t er 1 3 .5 1 95
F i re r ecords 1 3 .6 1 96
Re g is t e r o f Roads , Path s a nd Bu i ld ings 1 3 .7 1 96
Re s in Tapp ing Mon itor ing 1 3 .8 1 96
19
C H A P T E R – X I V
F I N A N C I A L F O R E C A S T
F i n a n c i a l F o r e c a s t 1 4 . 1 1 9 7 - 2 0 0
C H A P T E R - X V
S U M M A R Y O F P R E S C R I P T I O N S
S u m m a r y o f p r e s c r i p t i o n a n d s u g g e s t i o n s 1 5 . 1 2 0 1
C h i l S h e l t e r w o o d W o r k i n g C i r c l e 1 5 . 2 2 0 1
C o p p i c e W o r k i n g C i r c l e 1 5 . 3 2 0 1
T h e P l a n t a t i o n W o r k i n g C i r c l e 1 5 . 4 2 0 1
P r o t e c t i o n W o r k i n g C i r c l e 1 5 . 5 2 0 2
K h a i r ( o v e r l a p p i n g ) W o r k i n g C i r c l e 1 5 . 6 2 0 2
T h e B a m b o o W o r k i n g C i r c l e 1 5 . 7 2 0 2
T h e W i l d L i f e M a n a g e m e n t ( O v e r l a p p i n g ) W o r k i n g C i r c l e 1 5 . 8 2 0 2 - 2 0 3
T h e J F M ( O v e r l a p p i n g ) W o r k i n g C i r c l e 1 5 . 9 2 0 3
T h e N T F P W o r k i n g C i r c l e 1 5 . 1 0 2 0 3
M i s c e l l a n e o u s R e g u l a t i o n s 1 5 . 1 1 2 0 3
E s t a b l i s h m e n t a n d l a b o u r 1 5 . 1 2 2 0 3
C o n t r o l a n d R e c o r d s 1 5 . 1 3 2 0 3 - 2 0 4
F i n a n c i a l F o r e c a s t / S t a t e m e n t o f c o s t o f P l a n 1 5 . 1 4 2 0 4
D i g i t a l m a p s o f D e h r a F o r e s t D i v i s i o n a n d i t s R a n g e s ,
( A , B , C , D , E ) 2 0 5 - 2 0 9
L i s t o f S i g n a t o r i e s t o D e h r a W o r k i n g P l a n , ( F ) 2 1 0
A p p r o v a l o f W o r k i n g P l a n , ( G ) 2 1 1 - 2 1 2
20
Glossary of Botanical Names:-
S. No. Family Botanical Name Local Vernacular name
1 Acanthaceae Adhatoda zeylanica (=A. vasica) Basuti
2 Acanthaceae Strobilanthes auriculata Kapur minngar
3 Agavaceae Agave americana Ram ban
4 Amaranthaceae Deeringia amaranthoides (=D.
celosioides) Bhirang
5 Anacardiceae Lannea coromandelica Kehmal
6 Anacardiceae Mangifera indica Am
7 Anacardiceae Pistacia integerrima Kakrain
8 Anonaceae Miliusa velutina Chopar chilla
9 Apocynceae Carissa opaca Garuna
10 Apocynceae Holarrhena pubescens (=H.
antidysenterica)
Keor
11 Apocynceae Ichinocarpus frutescens
(=Quirivelia frutescens) Bakkarbel
12 Apocynceae Nerium oleander (=N. odorum) Ghanira Gandheela
13 Apocynceae Vallaris solanacea (=V. heynei) Dudh bel
14 Apocynceae Wrightia arborea (=W.
tomentosa) Khalawa
15 Arecaceae (=Palmae) Phoenix sylvestris Khajoor
16 Asclepiadaceae Calotropis procera Ak
17 Asclepiadaceae Cryptolepis buchananii Jaman khumb
18 Asclepiadaceae Dregia volubilis (=Wattakaka
volubilis) Mund bel
19 Asclepiadaceae Periploca calophylla Sarpri
20 Asclepiadaceae Tylophora hirsuta Terni
21 Asteraceae (=Compositae) Ageratum conyzoides Gha buti
22 Bignoniaceae Oroxylum indicum Tatplanga
23 Bignoniaceae Stereospermum chelonoides Padal
24 Bombacaceae Bombax cieba Simal
25 Cactaceae Opuntia elatior Chhittar Chhun
26 Caeselpinaceae Bauhinia malabarica Kacnnar, Karal
27 Caeselpinaceae Bauhinia purpurea
28 Caeselpinaceae Bauhinia vahlii Taur
29 Caeselpinaceae Bauhinia variegata Kachnar, Karal
30 Caeselpinaceae Caesalpinia decapetala Ralan, Arlu
31 Caeselpinaceae Cassia fistula Kaniar Amaltas, Alis
32 Caeselpinaceae Cassia occidentalis Chakunda
33 Caeselpinaceae Cassia tora Panwar
34
Cannabinaceae Cannabis sativa Bhang
35 Capparaceae Capparis sepiaria Hiun garna
36 Capparaceae Crataeva religiosa Barna
37 Celastraceae Cassine glauca Mirgu
21
38 Celastraceae Celastrus paniculatus Sankhiran
39 Celastraceae Euonymus pendulus Bharmela
40 Celastraceae Maytenus royleana
(=Gymnosporia royleana)
Bhadrun
41 Combretaceae Anogeissus latifolus Dhao. Chhal
42 Combretaceae Terminalia alata (=T. tomentosa) Asian Sain
43 Combretaceae Terminalia arjuna Arjan
44 Combretaceae Terminalia bellirica Bahera
45 Combretaceae Terminalia chebula Harar
46 Convolvulaceae Argyreia nasirii (=Lettsmia
thomsonii)
47 Convolvulaceae Ipomoea turpethum
48 Convolvulaceae Porana paniculata Faindal
49 Cuscutaceae Cuscuta reflexa Agas bel
50 Dioscoreaceae Dioscorea belophylla
51 Dioscoreaceae Dioscorea bulbifera
52 Dioscoreaceae Dioscorea deltoides Jung kinch
53 Dipterocarpaceae Shorea robusta Sal
54 Ebenaceae Diospyros chloroxylon Kinnu
55 Ebenaceae Diospyros cordifolia Kala dhao
56 Ebenaceae Diospyros montana Kendu
57 Ehretiaceae (=Cordiaceae) Cordia dichotoma (=C. myxa) Lasura
58 Ehretiaceae (=Cordiaceae) Cordia vestita Kumbhi
59 Ehretiaceae (=Cordiaceae) Ehretia acuminata Sakar
60 Ehretiaceae (=Cordiaceae) Ehretia laevis Chamorar
61 Euphorbiaceae Antidesma acidum Amla
62 Euphorbiaceae Bischofia javanica Marak
63 Euphorbiaceae Bridelia squamosa Gaddi
64 Euphorbiaceae Drypetes roxburghii (=Putranjiva
roxburghii)
Putajen
65 Euphorbiaceae Euphorbia royleana Kuri Thor, Chhun
66 Euphorbiaceae Glochidion velutinum Chamar-saman
67 Euphorbiaceae Jatropha curcas Jamnota
68 Euphorbiaceae Mallotus philippensis Kamal
69 Euphorbiaceae Phyllanthus emblica (=Emblica
officinalis)
Amla
70 Fabaceae Abrus precatorius Rattak
71 Fabaceae Butea monosperma Dhak, Plah
72 Fabaceae Cajanus volubilis (=Atylosia
crassa) Bantaur
73 Fabaceae Dalbergia sissoo Shisham Tali
74 Fabaceae Desmodium motorium Dudli
75 Fabaceae Desmodium velutinum Jagru
76 Fabaceae Erythrina glabrescens Pariara Paliaro
77 Fabaceae Flemingia semialata Bara Solpan
22
78 Fabaceae Indigofera dosua Kathi
79 Fabaceae Milletia extensa Salangan
80 Fabaceae Mucuna pruriens Gajal bel
81 Fabaceae Ougeinia ougeinensis Sandan, Sanan
82 Fabaceae Pongamia pinnata (=Derris
indica) Sukhchain
83 Fabaceae Pueraria tuberosa Salod
84 Flacourtiaceae Casearia elliptica Chilla
85 Flacourtiaceae Flacourtia indica (=F. ramontchi) Kangu
86 Flacourtiaceae Xylosoma longifolium Chirandi
87 Juglandaceae Engelhardtia spicata var.
colebrookiana Samma
88 Lamiaceae (=Labiatae) Colebrookia oppositifolia Dusen
89 Lamiaceae (=Labiatae) Pogostemon plectranthoides Kali basuti
90 Lamiaceae (=Labiatae) Roylea cinearea Kararoi Tila pati
91 Lauraceae Persea gamblei Badrol
92 Liliaceae Asparagus racemosus Satmuli, Musli
93 Linaceae Reinwardtia indica Basant
94 Loranthaceae Dendrophthoe falcata Parand
95 Lythraceae Woodfordia fruticosa (=W.
floribunda)
Dhawin, Dhawi
96 Malpighiaceae Aspidopterys wallichii Jugter Dhur bel
97 Malpighiaceae Hiptage benghalensis (=H.
madablota) Malti wan
98 Malvaceae Urena lobata Unga
99 Meliaceae Azadirachta indica Nim
100 Meliaceae Melia azedarach Drek,Dek,Bakain
101 Meliaceae Toona ciliata Tun Tun
102 Menispermaceae Cocculus laurifarius Paror
103 Menispermaceae Stephania elegans Batindu
104 Mimosaceae Acacia catechu Khair
105 Mimosaceae Acacia leucophloea Reru, Riur
106 Mimosaceae Acacia modesta Phalai
107 Mimosaceae Acacia nilotica spp. indica Kikar
108 Mimosaceae Albizia chinensis Ohi
109 Mimosaceae Albizia lebbeck Siris, Sarin
110 Mimosaceae Albizia odoratissima Karmaru
111 Mimosaceae Mimosa himalayana Dargarhi
112 Moraceae Ficus benghalensis Barh, Bohar
113 Moraceae Ficus hispida Dagur
114 Moraceae Ficus nemoralis Dudla
115 Moraceae Ficus palmata Dura, Dogla
116 Moraceae Ficus racemosa (=F. glomerata) Rumbal
117 Moraceae Ficus religiosa Pipal
118 Moraceae Ficus rumphii Palakh
23
119 Moraceae Ficus sarmentosa (=F. foveolata) Rudhar
120 Moraceae Ficus semicordata(=F. cunia) Kandroi
121 Moraceae Ficus subincisa (=F. clavata) Karanda
122 Moraceae Ficus virens (=F. infectoria) Padari
123 Moraceae Morus alba Tut
124 Moraceae Morus australis Sia-tut
125 Moraceae Morus macroura (=M. laevigata) Shah-tut
126 Moraceae Morus serrata Karun (cultivated)
127 Moringaceae Moringa oleifera Sanan Suhanjua
128 Myrsinaceae Ardisia solanacea
129 Myrsinaceae Maesa indica Burkani
130 Myrsinaceae Myrsine africana Chhota mendhru
131 Myrtaceae Careya arborea Handabhera
132 Myrtaceae Eugenia jambolana var.
caryophyllifolia Kathaman
133 Myrtaceae Syzygium cumini Jaman
134 Oleaceae Jasminum arborescens Dhur-malti
135 Oleaceae Jasminum dispermum Sarain
136 Oleaceae Jasminum grandiflorum Malti
137 Oleaceae Jasminum multiflorum Banmalti
138 Oleaceae Linociera intermedia Masandaru
139 Oleaceae Nyctanthes arbor-tristis Kuri, Hurshjngar
140 Oleaceae Olea ferruginea Kao
141 Pinaceae (=Coniferae) Pinus roxburghii Chil
142 Poaceae (=Gramineae) Artistida adscensionis (=A.
depressa)
Lambi
143 Poaceae (=Gramineae) Bambusa arundinacea Magar(Cultivated)
144 Poaceae (=Gramineae) Chrysopogan montana Dholu
145 Poaceae (=Gramineae) Cymbopogan martinii Makora gha
146 Poaceae (=Gramineae) Dendrocalamus hamiltonii Mohar (Cultivated)
147 Poaceae (=Gramineae) Dendrocalamus strictus Bans Bain
148 Poaceae (=Gramineae) Eulaliopsis binata Bhabar, Bagar
149 Poaceae (=Gramineae) Hetropogon contortus Lambu
150 Poaceae (=Gramineae) Saccharum spontaneum Kahi
151 Poaceae (=Gramineae) Sorghum nitidum Lunji
152 Punicaceae Punica granatum Anar, Doran
153 Raunnanculaceae Clematis gouriana Jhol
154 Raunnanculaceae Clematis grata Charki
155 Raunnanculaceae Clematis roylei (=C. nutans) Coibru, Machrun
156 Rhamnaceae Rhamnus triqueter Gulodan
157 Rhamnaceae Sageretia filiformis (=S.
oppositifolia)
Girgithan
158 Rhamnaceae Zizyphus mauritiana (Z. jujuba) Ber
159 Rhamnaceae Zizyphus oenoplia Kokal-ber
160 Rosaceae Pyrus pashia Kainth
24
161 Rosaceae Rubus niveus (=R. lasiocarpus) Kala akha
162 Rosaceae Rubus paniculatus Akha
163 Rubiaceae Catunaregam spinosa (=Randia
dumetorum)
Rara
164 Rubiaceae Himalrandia tetrasperma
(=Randia tetrasperma) Jindru
165 Rubiaceae Hymenodictyon orixense (=H.
excelsum)
Barthua
166 Rubiaceae Mitragyna parvifolia Kalan
167 Rubiaceae Spermadictyon sauveolens
(=Hamiltonia suaveolens) Gullhain
168 Rubiaceae Wendlandia heynei Pansera
169 Rutaceae Aegle marmelos Bil
170 Rutaceae Murraya koenigii Gandhla
171 Rutaceae Murraya paniculata Nargan
172 Rutaceae Naringi crenulata (=Limonia
acidissima)
Barnahi Billan
173 Salicaceae Salix tetrasperma Badhla
174 Santalaceae Osyris wightiana Sason
175 Sapindaceae Dodonaea viscosa Maindhor
176 Sapindaceae Sapindus mukorossi Ritha
177 Sapotaceae Madhuca indica Mahua (introduced)
178 Saurauiaceae Saurauia napaulensis Bhakara
179 Sterculiaceae Helicteres isora Maror phalli
180 Tiliaceae Grewia eriocarpa (=G. elastica) Phalsa
181 Tiliaceae Grewia optiva (G. oppositifolia) Biul, Dhaman
182 Tiliaceae Grewia serrulata (=G. laevigata) Dhamriana Damani
183 Ulmaceae Holoptelea integrifolia Rajain, Pardesi
184 Ulmaceae Trema politoria Kasa Kuri
185 Urticaceae Boehmeria platyphylla Padara
186 Urticaceae Boehmeria rugulosa Ligga
187 Verbenaceae Callicarpa macrophylla
188 Verbenaceae Caryopteris odorata Ban-basuti
189 Verbenaceae Clerodendrum phlomidis Dhakkari
190 Verbenaceae Gmelina arborea Ban
191 Verbenaceae Lantana camara Lantana, Ukkal Buti,
Panjphulli
192 Verbenaceae Premna barbata Ginani
193 Verbenaceae Premna mucronata Bhankahar, Gin
194 Verbenaceae Tectona grandis Sagwan (introduced)
195 Verbenaceae Vitex negundo Bana
196 Vitaceae Ampelocissus latifolia Giddar Dakh
197 Vitaceae Cayratia trifolia Chamar bel
198 Vitaceae Vitis flexuosa (=V. parvifolia)
25
LIST OF ANIMALS, LOCAL BIRDS AND MIGRATORY BIRDS:-
Sr.
no Name 0f Species Sr.no Name 0f Species Sr.
no Name 0f Species
1 Common Pochard 51 Common Merganser 101 Common crow
2 Bar-headed Goose 52 Black-winged Stilt 102 Red jungle fowl
3 Northern Pintail 53 Median (Intermediate) Egret 103 Common sparrow
4 Common Coot 54 Lesser Whistling Duck 104 Lizard
5 Great Cormorant 55 White-breasted Waterhen 105 Monitor
6 Common (Green-winged)
Teal 56
Green Sandpiper 106
Viper Snake
7 Litte Cormorant 57 Citrine Wagtail 107 King cobra snake
8 River Tern 58 Paddyfield Pipit 108 Barking deer
9 Tufted Pochard 59 Black Kite 109 Squirrel
10 Gadwall 60 White-breasted Kingfisher 110 Porcupine
11 Black-headed Gull
61 Great Stone Plover/ Great Thick
Knee 111
Rodents
12 Northern Shoveler 62 Black-bellied Tern 112 Leopard
13 Temminck’s Stint 63 Lesser Pied Kingfisher 113 Sāmbhar
14 Brown-headed Gull 64 Eurasian (White) Spoonbill 114 Common Monkey
15 Eurasian Wigeon 65 Greater White Fronted Goose 115 Eagle
16 Little Egret 66 Pied Avocet 116 King Fisher
17 Brahminy (Ruddy)
Shelduck 67
Marsh Sandpiper 117
Rabbit
18 Purple Swamphen 68 Common Snipe
19 Spot-billed Duck 69 Water Pipit
20 Little Grebe 70 Indian Pond Heron
21 Moorhen 71 Osprey
22 Mallard 72 Purple Heron
23 Sand Lark 73 Grey Wagtail
24 Little ringed plover 74 Tawny Pipit
25 Great Crested Grebe 75 Oriental Darter
26 Greylag Goose 76 Ferruginous Pochard
27 Pallas’s Gull 77 Sarus Crane
28 Crested Lark 78 Pheasant-tailed Jacana
29 White Wagtail 79 White-tailed Lapwing
30 Common Swallow 80 Wood Sandpiper
31 Yellow Wagtail 81 Greater Pied Kingfisher
32 Common Sandpiper 82 Western Reef Egret
33 Common Greenshank 83 Black-necked Grebe
34 Little Tern 84 Indian Shag
35 Kentish Plover 85 Painted Stork
36 River Lapwing 86 Garganey
37 Unidentified Cormorants 87 Spotted Redshank
38 Red-wattled Lapwing 88 Little Stint
39 Grey Heron 89 Rosy Pipit
26
40 Northern Lapwing 90 Black Bittern
41 Oriental Sky Lark 91 White-necked Stork
42 Cattle Egret 92 Eurasian Thick Knee
43 Slender-billed Gull 93 Western Marsh-Harrier
44 Large (Great) Egret 94 Red-throated Pipit
45 Red-crested Pochard 95 Blyth's Pipit
46 Eurasian Sky lark 96 Magpie
47 Common Redshank 97 Albatross
48 Gull-billed Tern 98 Parrot
49 Large Pied/White Browed
Wagtail 99
Pigeon
50 Common Shelduck 100 vulture
27
Glossary of local terms:-
Local term English Equivalent
A b a d i H a b i t a t i o n
A d n a m a l i k I n f e r i o r o w n e r
A l a m a l i k S u p e r i o r o w n e r
A l a m a l k i a t S u p e r i o r o w n e r s h i p
A s a m i T a n a n t
A s u j I n d i a n m o n t h b e t w e e n 1 5t h
O c t .
t o 1 5t h
N o v .
B a g h P a n t h e r
B a n s a r k a r G o v e r n m e n t F o r e s t s
B a r t a n R i g h t o f u s e r s
B a r t a n d a r R i g h t - h o l d e r
B h a t t i F u r n a n c e
B h u t a r T h e d o m e s t i c c a t t l e t u r n e d w i l d
C h a l L a b o u r w h o s u p e r v i s e s
m a n u f a c t u r e o f k a t h a
C h a k P l a c e o f l a n d
C h a k S h a m l a t D e h A p l a c e o f B a n S a r k a r a r e a s u r r o u n d e d
b y D P F & R e s e r v e d F o r e s t s
C h a r a n d G r a z i n g g r o u n d
C h o k i d a r A v i l l a g e w a t c h m a n
D h a r R i d g e
G a d d i s A c o m m u n i t y o f m i g r a t o r y g r a z i e r s
k e e p i n g s h e e p , g o a t
G h a s n i H a y l a n d
G o d a m G r a s s p r e s e r v e
G u j i a r A c o m m u n i t y o f m i g r a t o r y g r a z i e r s
k e e p i n g r e a r i n g b u f f a l o e s
H a r r I n d i a m o n t h b e t w e e n 1 5 t h J u n e
28
t o 1 5T h
J u l y
H a t h H a n d l e n g y h 4 5 c m
E x - J a g i r T r a c t o f l a n d , f r o m w h i c h t h e
G o v t . r e v e n u e w a s C o l l e c t e d
t h r o u g h t h e P o w e r o f t h e
a d m i n i s t r a t o r
J a g i r d a r T h e h o l d e r o f s u c h a s s i g n m e n t
J a m a b a n d i V i l l a g e r e v e n u e r e c o r d
K h a d A s t r e a m p e r e n n i a l o r s e a s o n a l
K h a s a r a A f i e l d n u m b e r g i v e n i n t h e v i l l a g e
r e v e n u e r e c o r d
K a t h a T a n n i n o b t a i n e d f r o m k h a i r t r e e s
K h e w a t d a r L a n d h o l d e r
M a i A w o o d e n s l a b d r a w n b y b u l l o c k s &
u s e d f o r t h e s o i l p r e s s i n g
T h e p l o u g h e d f i e l d
M a l k a n a P r o p r i e t a r y r i g h t
M a u z a A u n i t c o n s t i t u t e d b y a n u m b e r o f
t i k a s f o r t h e p u r p o s e o f r e v e n u e
C o l l e c t i o n
M a z d o o r L a b o u r e r
M o h a l A r e v e n u e e s t a t e
M u g a l M o h a m m e d a n a d m i n i s t r a t i o n
N a u t o r B r e a k i n g o f l a n d f o r c u l t i v a t i o n o r
h a b i t a t i o n f o r t h e f i r s t
N a l a A s m a l l w a t e r c h a n n e l o r a t o r r e n t
P a t r a h L e a v e s o f b r o a d l e a v e d t r e e s
P a t w a r A g r o u p o f v i l l a g e s f o r m i n g a
p a t w a r c i r c l e
P a t w a r i A r e v e n u e o f f i c i a l i n c h a r g e o f a
p a t w a r c i r c l e
R a j a A r u l e r
R a k h a W a t c h e r
S h a m l a t V i l l a g e c o m m o n l a n d
29
S o w a n a L a r g e b l a n k i n a f o r e s t u s e d f o r
g r a z i n g
T a l u k a R e v e n u e c i r c l e , a t r a c t o f
p r o p r i e t a r y l a n d
T a p p a I t i s s y n o n y m o f m a u z a
T i k a I t i s s y n o n y m o f m o h a l
T i r n i G r a z i n g d u e s
T r i h a i O n e t h i r d o f a r e a u n d e r c l o s u r e
W a j u b - u i - a r z R e c o r d o f r i g o t s
Z a m i n d a r L a n d o w n e r
30
ACRONYMS AND ABBREVIATIONS
Sr.
No.
Symbol Full form
1 F D Forest Department
2 WC Working Circle
3 MNREGA Mahatma Gandhi National Rural Employment Guarantee Act.
4 JFMC Joint Forest Management Committee
5 SHGs Self Help Groups
6 NPV Net Present Value
7 DPF Demarcated Protected Forest
8 UPF Un demarcated Protected Forest
9 UCF Un Classified Forest
10 RF Reserved Forest
11 Cm Centimeter
12 Dia Dia meter
13 Dbh Diameter at brest height
14 FS Felling series
15 LB Left bank
16 RB Right bank
17 N. Surian Nagrota Surian
18 J. Mukhi Jawala Mukhi
19 D Siba Dada Siba
20 C Fs Community Forests
21 B L Broad leave
22 ACF Assistant Conservator of Forests
23 DFO Divisional Forest Officer
24 MoEF Ministry of Environment and Forests
25 GoI Government of India
26 WL Wild life
27 IUCN International Union for Conservation of Nature
28 MSL Mean See level
29 DFID Department for International Development
30 VFDC Village Forest Development Community
31 FMP Forest Management Plan
32 SVY Sanjhi Van Yojna
33 NGO/CBO Non Governmental Organization/Community Based Organization
34 LC Least concern
35 EN Endangered
31
ACRONYMS AND ABBREVIATIONS(continue)
Sr.
No.
Symbol Full form
35 CR Critically Endangered
36 VU Vulnerable
38 NT Near threatened
40 JK Jammu & Kashmir
41 NW North- West
32
VOLUME-I
PART –I
SUMMARY OF FACTS ON WHICH
THE PROPOSALS ARE BASED
33
C H A P T E R - I
T H E T R A C T D E A L T W I T H
1: NAME AND SITUATION:
1.1 This working plan deals with the forests of the territorial jurisdiction of Dehra Forest
Division. Dehra Forest Division was notified in the year 1984 vide Govt. notification. Prior to its
constitution, the forests of this division were being dealt with two Forests Divisions. The forests of
right bank of the river Beas were with Dharamsala Forest Division and were being dealt under M.P.
Singh’s working plan, where as forests on the left bank of the river Bias were with Una Forest
Division and were being dealt under Baldev Singh’s Plan.
1.2 Dehra Division includes the area of Dehra Sub Division (Civil) and part of Jawali Sub-division
(Civil) and falls in Kangra district of Himachal Pradesh. Further for the territorial control it falls
under jurisdiction of Hamirpur forest circle. Dehra Forest Division is situated between longitude 75o
45’ E to 76o
52’ 30” E latitude 31O 43’N to 32
o 30’N. In the north of this Division lies Dharamshala
Division and part of Nurpur Division, In the East it is surrounded by Palampur Forest Division.
Hamirpur Forest Division lies to its south where as Una Forest Division & a part of Nurpur Forest
Division make the western boundary of this division.
The geographical area of this division is 1200 Km2 (appox.) and the net forest area is 300 km
2 which
is 25% of total geographic area. The headquarters of Dehra Forest Division is at Dehra.
1 . 2 : C O N F I G U R A T I O N O F T H E G R O U N D :
1.2.1 The altitude of the tract varies from 340 meter to 950 meters above mean sea level, the
lowest point being at Sansarpur in Dadasiba Range and the highest point situated near Habrol in
Jawalamukhi Range of this division. The configuration varies from steep slopes to gentle hill slopes
with network of small rivers and big river like Beas which meet the water requirement of the area
for irrigation at least for the major part of the year. Small rivers usually remain dry except rainy
season which is July and August months and cause lot of soil erosion problem.
1.3: GEOLOGICAL ROCK AND SOIL:
1.3.1 The various geological formations encountered in the Dehra Forest Division are described
below
1.3.2 UPPER SHIVALIKS
The rocks of the Shivalik system occupy a thick belt and are seen around Dehra Gopipur and
Jawalamukhi areas and run in a NW direction of Dadasiba. These formations occupy the major
portion of the division and are composed of grey soft friable, coarse grained sand stone with bands
of greyish green and purple clay. These are inter-bedded with boulder beds. Boulders are poorly
cemented and quartzitic in nature.
1.3.3 PINJOR BOULDERS BED
These in admixture with conglomerates are met between Aloh in SE and Sansarpur in the SW and
also up to Baldoa and Amblela areas at the Northern limit of the Division. The composition of these
boulders is loose sand and prone to weathering.
1.3.4 GEOLOGY OF DEHRA:
The Geological survey of India, Chandigarh has supplied the information and the same is depicted
below:
Dehra Gopipur is a tehsil in Kangra district and it is bounded by longitude 75o
45’ E to 76o
52’ 30” E
latitude 31O 43’N to 32
o 30’N . The various rock types exposed in Dehra tehsil belong to lower
middle and upper Shivalik of middle Miocene to Pliocene ages and alluvium of quaternary age. The
34
lower Shivalik consists of red and purple sand stone and shale; Middle Shivalik of grey sand stone
and orange colour clay, whereas upper Shivalik is made of soft sand stone with Arkose brownish
clay, purely sorted and cross bedded conglomerate and boulder bed. The major structure in the
area is the Dehra Gopipur auto-cline. Taxonomic unit of soil are typic udorthenth and dystric
eutrochrepts. Typical underneath soil, medium deep well dystric thermic coarse loamy soil and
gentle slope with moderate erosion, whereas dystric eutrochrapts soil is medium deep well
drained, fine to medium loamy soil with loamy surface and moderate erosion.
1.4: SOIL AND FOREST DISTRIBUTION:
The Shivalik system of rocks yields soil of sandy to loamy structure and supports low quality chil
and scrub forests. These soils are generally dry and deficient in organic matter. Development of soil
profiles over most of the tract is not clearly discernible. The North West slopes have clays which
alternate with sandstones. Alluvial deposits along streams have deep fertile sandy loam to clayey
loam soils where pioneer species like Khair, Dalbergia and Salmalia flourish.
1.5: CLIMATE:
Since this Division lies between longitude 75o
45’ E to 76o
52’ 30” E latitude 31O 43’N to 32
o 30’N, its
climate is subtropical type. The seasons are well defined. Mid of Feb. to March end and Oct- Nov.
are pleasant. May to mid June is very hot and mid June to mid September the area experiences
heavy rain. Summer season is usually full of sand dust laden winds. The entire belt is almost rain
fed. Summers are usually dry and area experiences acute shortage of water.
Table 1: (Rain data in mm month) Dehra Gopipur
Table 2: Some rainfall data, decadal averages in mm, since 1891-92 is available for Dharamsala,
Kangra and Dehra stations and is reproduced below: (from MP Singh’s WP):
Year Jan. Feb. Mar. April May June July Aug. Sept. Oct. Nov. Dec. Total
1984 14.50 112.60 17.00 ----- ------ ------- 332.20 322.90 145.90 ------ ------ 25.50 970.60
85 54.50 4.20 5.40 16.20 4.00 102.20 482.10 438.30 192.10 103.30 ------ 74.00 1476.30
86 Nil 96.00 52.70 25.00 63.90 95.20 415.50 465.60 14.20 59.00 68.20 43.80 1399.10
87 90.00 59.20 31.00 39.90 212.60 79.70 241.70 236.70 99.00 71.40 ------ 6.20 1167.40
88 27.60 76.00 103.60 3.60 28.00 69.50 589.40 359.30 558.20 ------ 1.20 77.30 1893.70
89 99.20 29.00 61.40 11.60 22.40 60.20 384.90 272.50 46.60 ------ 49.20 70.80 1107.80
90 8.20 96.20 119.90 16.20 37.40 57.50 308.40 424.80 396.60 4.20 -------- 131.30 1600.70
91 ---- 70.20 52.00 53.80 20.00 36.30 166.30 485.10 178.80 8.00 -------- 89.90 1160.40
92 115.40 78.30 47.30 3.50 30.90 61.00 397.50 900.80 37.60 ----- 14.40 1.50 1688.20
93 66.90 3.70 60.00 3.00 14.10 115.00 648.30 141.80 130.60 ----- 3.50 ------ 1186.90
1365.11
94 62.10 74.30 5.10 64.90 33.30 163.00 629.40 765.70 55.70 5.40 -------- 40.40 1899.30
95 44.50 116.50 44.20 24.10 -------- 26.00 440.30 465.50 5.20 ----- 5.00 2 1173.30
96 52.00 89.20 58 7.00 31.00 229.70 288.50 410.30 97.00 39.50 ------- 1.40 1303.60
97 68.50 55.30 49.80 85.90 39.20 135.40 573.90 571.50 165.20 16.70 87.50 81.50 1930.40
98 10.40 184.70 180.20 77.00 13.00 110.10 246.10 328.90 157.90 78.50 0.70 -------- 1387.50
99 63.40 11.90 7.60 ------ 119.80 86.70 544.70 515.20 99.90 1.40 9.20 0.20 1460.00
2000 109.00 105.00 51.10 11.00 93.90 169.10 588.00 99.50 149.00 ------- 16.50 1392.10
2001 8.20 6.40 39.10 ------- -------- -------- ------- ------ ------ -------- ------ --------
2002 21.00 10.60 29.60 16.60 6.60 81.00 154.00 437.00 126.40 13.00 0 1.20 897.00
2003 32.20 124.20 81.00 7.20 9.00 75.60 235.50 532.70 243.50 0 3.00 9.60 1353.50
2004 77.20 13.90 0 16.70 36.60 95.50 233.00 122.00 109.90 94.20 5.20 15.80 820.00
2005 46.40 115.20 70.60 8.40 1.00 12.20 338.80 168.60 75.40 0 0 0 836.60
2006 22.00 71.80 63.60 2.00 33.60 164.00 577.80 376.00 141.00 42.20 7.30 23.20 1524.50
2007 0 70.20 179.80 38.80 35.40 146.30 337.90 355.80 133.20 1.50 0.20 23.10 1322.20
2008 40.30 23.20 0 19.00 19.20 579.30 460.10 488.35 85.55 37.40 0 1.20 1753.60
2009 36.60 38.70 16.30 69.20 23.80 38.60 405.10 232.10 111.30 0 49.80 0 1021.50
2010 11.80 32.30 9.00 0.40 37.30 86.10 296.70 250.00 160.30 55.20 4.00 49.00 992.10
35
Years Dharamsala Kangra Dehra Gopipur
1891-92 to 1918-19 3020.82 2022.09 1425.19
1919-20 to 1929-30 2932.93 1917.95 1263.14
1930-31 to 1950-51 3417.06 2019.04 1300.60
1951-52 to 1955-56 NA NA NA
1956-57 to 1966-67 3323.30 2038.10 1230.00
1966-67 to 1980-81 3385.53 1944.16 1522.02
1984 to 1993 1365.11
1994 to 2003
2004 to 2011
T a b l e 3 : T E M P E R A T U R E
Year January February March April
Max Min Max Min Max Min Max Min
1995 21.5 6 24 7 32 8 36 13.5
1996 23 6.5 24.5 9 31 12 38 15
1997 21.5 6 34 6 30 11.5 37.5 13
1998 21 6 23.5 8 27 11 27.5 14
1999 21.5 6.5 24 7 34 10 42 16.5
2000 22.5 5 25 6.5 33 9 40 15.5
2001 25 3.5 27.5 5.5 32 9 38.5 14
2002 22.5 5.5 28 5.5 33 9 39 16
2003 22.5 3.5 25 7.5 31 6.5 40 15.5
2004 23.5 6 29.5 6 35.5 12 41 17.5
2005 21.5 5 24.5 6 30 11 38 14
2006 25 4.5 30.5 8.5 31 10 42.5 13
Year May June July August
Max Min Max Min Max Min Max Min
1995 42.5 20.5 45.5 18.5 39.5 22 34.5 22
1996 41.5 16 42.5 20 35.5 21 37 21.5
1997 40.5 16.5 40 18 40 21 35.5 20
1998 44 18 43 19 37 22.5 35 22.5
1999 43 18 40 21.5 37.5 21 35.5 21
2000 41.5 19 40 17.5 37 18 35.5 21
2001 34.5 20 41.5 20 35 21 35.5 21
2002 44 19.5 44 21 40 21 35 21
2003 41 16 44.5 20.5 36.5 20 35 18
2004 46 15 43.5 19 39 22 35 18.5
2005 42 18 46..5 20 37.5 36.9 22.5
2006 43.5 18 43 20 37.5 21.5 37 21.5
Year September October November December
Max Min Max Min Max Min Max Min
36
1995 35 19 34.5 17 30 11 24 8
1996 35.5 20 32.5 17 30 11 24 6.5
1997 34.1 19 31 15 27 11 27 11
1998 34.5 19.5 35.2 17 27.5 11 26.5 7
1999 34.5 21 33 16 32 10 25 6.5
2000 35 19.5 33.5 18 28 10 25.5 7.5
2001 35 19 34 18
2002 33.5 19 33.5 14 28.5 11 24.5 7
2003 34.5 19.5 30 17 28 9.5 25 6.5
2004 37 21.5 35.5 15 27.5 14 25 8
2005 36 21 33.5 16.5 28.5 11 23.5 5
2006 34.5 21 34 15.5 28.5 8 24 4.5
1.6: WATER SUPPLY:
1.6.1: Water supply for drinking purposes is generally met from the various perennial streams
/khads like Chanaur Khad, Badhal Khad, Dhaliara Khad, Kaloha Khad etc. throughout the tract.
Along motor-able roads near habitations, the IPH department has installed 150 hand pumps to
meet the drinking water requirement. In May 2001 a hand pump has been installed at Ranser
island in the Pong Lake. IPH has also installed 29 lift water irrigation schemes and 56 gravity water
supply schemes for irrigation purposes.
1.6.2: During summer, scarcity of water prevails over the larger part of the area. People have to
bring water for drinking purpose from long distances as many wells and natural springs dry up. The
situation has considerably improved along road side habitations due to the installation of hand
pumps. In case monsoon downpours are delayed, it leads to large-scale mortality in young
plantations.
1.7: DISTRIBUTION OF AREA: In the plan under Revision the total area of UPF of Dada Siba Range was taken as 4295.75 Ha;
whereas, in this plan the area is 4284.46 Ha. Reasons for difference of 11.29 Ha are discussed
below:
Difference in total in the plan under revision = 4295.75 – 4292.82 = 2.93 Ha.
The area in the following Forests/Compartment of Dada Siba Range UPF in the plan under Revision
was wrongly taken/printed which has now been corrected after consulting relevant record and CH
files.
The difference in UPFs of Dehra Range is due to inclusion of 57.01 ha of UPF Dhar Shham Forest in
this plan which has not been dealt in the earlier plan. Similarly, in the earlier Plan the total area of
UFs in Dehra Range was taken as 4324.68 wrongly. It is now 4602.68 Ha in this plan. The reason of
variation is wrong printing and totaling. U17D Bahungta (278 Ha) was not counted in the total area
has now been taken and area corrected. The forest/ compartment areas which have been
corrected in this plan after consulting the relevant records and CH files are:
Name of Forests of Dada
Siba Range
Compartment Area as per New Plan
(In Ha.)
UPF-33 Nari C4 50.88
UPF-44 Banuri C1 36.01
-do- C3 45.32
-do- C5 23.00
UPF 7 Gulardhar C4 2.53
37
The area dealt with in this working plan according to legal classification is tabulated range wise as
below: ( also see appendix-I)
T a b l e 4 : A r e a S t a t e m e n t ( H a )
T
T a b l e 5 : The detail of Seismic information is tabulated below:
DATE LATITUDE LONGITUDE DEP MAGNITUDE
2 6 - 7 - 9 3 3 2 . 1 0 9 7 6 . 3 1 4 8 . 2 1 3 . 3 1
5 - 1 2 - 9 3 3 2 . 2 5 7 6 . 3 1 7 1 2 3 . 4 7
2 1 - 8 - 9 4 3 2 . 2 5 7 6 . 3 1 7 1 2 3 . 6 7
2 8 - 8 - 9 4 3 2 . 2 8 6 7 6 . 2 9 7 1 6 . 5 2 2 . 7 6
2 3 - 9 - 9 4 3 2 . 2 0 1 7 6 . 1 9 3 3 0 . 1 5 3 . 3 7
2 4 - 9 - 9 4 3 2 . 2 5 7 6 . 3 1 7 1 2 3 . 3 3
2 4 - 1 - 9 5 3 2 . 4 0 7 7 6 . 1 8 1 1 6 . 6 4 3 . 0 3
2 4 - 8 - 9 5 3 2 . 2 5 7 6 . 3 1 7 1 2 3 . 5 6
2 3 - 1 0 - 9 5 3 2 . 0 4 4 7 6 . 2 6 3 1 2 3 . 7 2
1 5 - 1 1 - 9 5 3 2 . 2 5 7 6 . 3 1 7 1 2 3 . 4 8
2 3 - 2 - 9 6 3 2 . 4 5 2 7 6 . 2 7 3 5 . 6 1 2 . 7 2
1 5 - 5 - 9 6 3 2 . 2 5 7 6 . 3 1 7 1 8 . 6 9 2 . 9 1
2 5 - 5 - 9 6 3 2 . 4 9 7 7 6 . 2 0 7 1 7 . 9 8 2 . 2 7
2 7 - 5 - 9 6 3 2 . 4 6 7 7 6 . 3 3 1 3 2 . 9 3 2 . 4 4
5 - 7 - 9 6 3 2 . 4 0 7 7 6 . 3 1 7 1 2 2 . 6 0
4 - 1 0 - 9 6 3 2 . 4 8 1 7 6 . 3 3 3 2 4 . 3 8 2 . 3 6
1 3 - 1 0 - 9 6 3 2 . 4 5 8 7 6 . 2 1 6 7 . 4 1 2 . 5 5
2 1 - 1 0 - 9 6 3 2 . 4 1 8 7 6 . 1 3 3 1 2 4 . 0 2
3 0 - 1 0 - 9 6 3 2 . 4 9 5 7 6 . 2 0 9 2 0 . 7 8 3 . 7 5
2 - 1 1 - 9 6 3 2 . 2 5 7 6 . 1 3 5 1 1 2 . 3 4
4 - 1 1 - 9 6 3 2 . 3 7 7 7 6 . 2 7 9 1 2 3 . 7 8
5 - 1 1 - 9 6 3 2 . 4 7 6 . 3 2 4 1 2 3 . 4 8
5 - 1 1 - 9 6 3 2 . 2 5 4 7 6 . 2 8 3 1 2 3 . 8 8
7 - 1 1 - 9 6 3 2 . 4 3 2 7 6 . 3 3 9 1 2 3 . 3 0
1 2 - 1 1 - 9 6 3 2 . 0 4 4 7 6 . 2 6 3 1 2 4 . 4 3
1 5 - 1 1 - 9 6 3 2 . 3 5 2 7 6 . 2 5 4 1 8 . 7 4 . 2 5
1 9 - 1 1 - 9 6 3 2 . 2 8 7 6 . 3 1 7 1 2 3 . 3 3
1 7 - 1 - 9 7 3 2 . 3 9 7 6 . 3 3 8 1 6 2 . 9 4
1 8 - 1 0 - 9 8 3 2 . 3 7 3 7 6 . 1 8 5 2 . 3 2 2 . 3 1
2 7 - 1 2 - 9 8 3 2 . 3 0 2 7 6 . 2 1 7 . 2 4 2 . 2 9
Name of Forests of
Dehra Range
Compartment Area as per New Plan (In
Ha.)
UF-67 Nari C1 26.93
UF-17 Bihan C4 27.49
Range RFs DPFs UPFs UCFs CSFs Road
strips
Rail
strips
G. Total
Dadasiba 122.23 1825.67 4284.46 273.39 6505.75
Dehra 1110.09 4602.68 2693.99 33.65 79.96 8577.39
J-mukhi 935.11 2488.97 5174.78 728.00 33.25 9360.11
N-Surian 574.97 911.33 229.04 3719.66 127.48 104.16 5666.64
G. Total 2742.40 2737.00 7059.49 13770.51 3549.47 66.90 184.12 30108.89
38
1.8: State of boundaries:
1.8.1 The last WP by Sh MP Singh noted: “The boundaries of Delimited Protected Forests are
suitably demarcated with large, numbered pillars of loose stone masonry at salient and re-entrant
points and with intermediate pillars of similar construction. The internal boundaries of
compartments and sub-compartments have been demarcated with small, loose stone masonry
pillars but are rarely found at present. Included cultivation is, however, not so demarcated. All the
un-delimited and un-classed forests, excepting where they adjoin private forests, are without
boundary pillar .Boundary pillars have gone into disrepair and have not been maintained”.
1.8.2: The boundaries of reserved forest and D.P.F’s have been well marked with boundary pillars.
But almost all the BPs are poorly maintained. The year wise expenditure incurred on the boundary
pillars is given below:
T a b l e 6 : E x p e n d i t u r e o n B P s
Y e a r E x p e n d i t u r e i n R u p e e s
1 9 9 5 - 1 9 9 6 3 0 , 2 0 0
1 9 9 6 - 1 9 9 7 1 5 , 0 0 0
1 9 9 7 - 1 9 9 8 2 2 , 0 0 0
1 9 9 8 - 1 9 9 9 1 5 , 8 0 0
1 9 9 9 - 2 0 0 0 2 0 , 8 0 0
2 0 0 0 - 2 0 0 1 2 0 , 2 0 0
2 0 0 1 - 2 0 0 2 2 0 , 4 0 0
2 0 0 2 - 2 0 0 3 2 0 , 6 0 0
2 0 0 3 - 2 0 0 4 4 0 , 8 0 0
2 0 0 4 - 2 0 0 5 1 8 , 3 0 0
2 0 0 5 - 2 0 0 6 0
2 0 0 6 - 2 0 0 7 3 5 , 0 0 0
2 0 0 7 - 2 0 0 8 2 7 , 6 7 5
2 0 0 8 - 2 0 0 9 1 7 , 3 0 0
2 0 0 9 - 2 0 1 0 2 1 , 7 0 0
1.8.3: The boundaries of un-demarcated protected forests are not so demarcated. As a result of
indeterminate nature boundary of such forests in the past, these are honeycombed with
cultivation and consequent chances of encroachments cannot be ruled out. These need proper
demarcation.
There are several areas that need to be addressed with reference to BPs here. (1) The forest wise BPs
need to be checked for number, whether they exist or not and the state of repair needs to be
recorded; (2) The BPs around “chaks” or enclosed cultivations are a priority; (3) Similarly, BPs of RFs
and DPFs which are prone to encroachment need to be identified. Thereafter, once we know the fore-
mentioned information / data, a year wise plan for proper repair or replacement of the BPs esp. in the
vulnerable RFs and DPFs has to be detailed in the WP.
Regular checking of boundaries and the boundary pillars is required to be followed as per the
quinquennial programme laid down in this plan under Miscellaneous Regulations Chapter.
39
1.9: LEGAL POSITION:
Land tenures, Land Revenue Settlement, Forest Schemes etc.
In order to have a fair idea of the present legal status of the forests, a detailed historical back
ground of the various measures taken in Kangra district as a whole is considered appropriate and is
therefore discussed as under:
Before commencement of the Mughal Rule, the Raja was the manorial lord of his territory which
was a single estate divided into a number of circuits for administration purposes. The circuits were
mere groupings of holdings under a Collector of rents. All waste land was the property of the Raja.
Every right was to come from the Raja; holding of land was derived from his grant. This system of
land tenure continued unchanged under the Mughal and Sikh Rulers till 1846, when the tract
ceded to the British.
1.9.1: Barnes land Revenue Settlement (1849—1852):
After cession of the territory in 1846, a summary settlement was carried out by John Lawrence.
Regular settlement was conducted by Barnes during 1849-52. Barnes converted each circuit, which
were collection of hamlets, with patches of cultivation and undefined rights of user in the
surrounding wastes, into ‘mauzas’ and demarcated their boundaries. Land holders of each mauza
were converted into a Co-proprietary body and Land Revenue was assessed at a lump-sum for the
entire mauza, the payment of which was made the joint responsibility of all the land holders of the
mauza. In order to balance the responsibility so imposed, these village Co-proprietary communities
were conferred with the right to collect and divide amongst themselves certain items of
miscellaneous revenue. The most important result from forest point of view was that the
ownership of the soil of the forests and the waste was transferred to the village co-proprietary
body with certain reservations of the rights of “Gaddi” shepherds and “Gujjar” herdsman; govt.
retaining only the ownership of the trees of spontaneous growth (Khudrao darkhtan) or planted by
it and the right to collect grazing dues from gaddis.
1.9.2: Ban Muafi and Un-classed Forests (1863):
In 1863 the govt. acquired 1030.53 ha of waste land to make it available to tea planters in 10
villages namely Bandla, Kusmal, Bbagotla, Kandi, Lanod, Dewal, Paprola, Bhattu, Jia, Chachiyan of
Palampur tehsil by granting to the village Co-proprietary body in each village complete ownership
of trees over an equivalent area and by abandoning its right to closure in the first 8 villages but
retaining the same in the last 2 villages. Therefore forests/waste lands in which government
surrendered all its rights were called “BAN MUAFIS” and were placed under the control of Deputy
Commissioner ; the remaining waste where only the right of closure was surrendered retaining
ownership of trees were designated as “Un-classed Forests”. Banmuafi forests are not found in
Dharamsala and Dehra Forest Divisions.
1.9.3: Lyall’s Reviesd land Revenue Settlement (1865-1869):
Sir James Lyall sub divided the mauzas (circuits) into Tikas consisting of one or more hamlets with
surrounding waste over which rights were claimed, defined and fixed boundaries of the Tikas
(Tikabandi). Thus Tika became the unit of revenue management. This was the most important
feature of Lyall’s operations. A large proportion of the waste was included within the tika
boundaries (on the basis of mutual agreement) the ownership of which was vested in the
Khewatdars of that tika and was recorded as “Shamlat tika”. The waste that could not be so
partitioned remained the joint property of the whole mauza and was recorded as “Shamlat Deh”.
Under the latter category fall:
40
(i) All or almost all the larger blocks of waste which were generally formed into separate tika
known as “Chakban” followed by the name of mauza (Chakbans are tikas containing nothing but
none or very little else than forest, and are the property of the whole mauza) and:
(ii) Certain small blocks of especially valuable forests which are shown in the maps of the tika
in which they fall. The proprietary right in Shamlat Deh is in proportion to the revenue paid by each
tika whereas in Shamlat tika it as a rule is proportional to the revenue paid by each Khewatdar.
However, there is an intermediate case, though not quite common, where the waste is the joint
property of a few and not of all the tikas of the mauza.
Lyall made certain proposals for forest conservancies which were never sanctioned, and thus apart
from an ambiguous definition of the lands Under Govt. forests and the conservancy clauses of the
administrative papers his settlement had little effect upon the forests.
1.9.4: Scheme of Roe and Duff (1872-1875): Reserved and Un-classed Forests:
On representation made by the Conservator of Forests in 1869, the Govt. appointed Roe
(Settlement Officer) along with Duff (Dy. Conservator of Forests) for demarcating absolute Govt.
forest areas. The principle to be followed was to acquire absolute proprietary rights in selected
areas in exchange for a modification of its rights in the remaining wastes. The scheme resulted in
the acquisition of complete rights over 3430.52 ha (8477 acres) in 21 villages of Nurpur tehsil, 3095
ha (7648 acres) in 29 villages of Dehra tehsil by way of granting special money and land
concessions, by abandoning the right of closure in the remaining waste and by conferring on the
village communities some special rights in such wastes. The land so acquired was notified as
Reserved Forests vide Notification No.111-F and 11’-F dated 6th March, 1879 and the remaining
wastes where the right of closure was abandoned were designated as Un-classed Forests. Rules for
preservation, protection etc of trees in Un-classed Forests were later on notified vide notification
No. 61 dated 26th Jan, 1897; subsequently amended vide No. 994 dated 11th Jan, 1919.
Fortunately further negotiations on these lines failed, the hazards of demarcation on these
principles realized and further demarcation on these lines was dropped. Considering the special
money and land concessions and the abrogation of the important right of closure, the result of the
measures described above can only be termed as disastrous to the forest conservancy.
1.9.5: Anderson’s Forest Settlement (1883-1897):
The regular forest settlement was carried out by Anderson in Kangra proper from 1883 to 1897
which was sanctioned in 1897. The principles on which the demarcation was carried out (para 5 of
his report), are as under:
(i) No change was to be made in the forest management of the forest land either
inside or outside the demarcation.
(ii) Forest land which should be permanently maintained as such was to be separated
by demarcation from forest land in which clearance for cultivation might at
sometime be permitted.
(iii) There were to be no give and take negotiations with the Zamiadars nor was the
demarcation to proceed with the idea that the forests excluded from it would be
made over to the Zamindars and released from all control.
Anderson did not deal with the Reserved and the Un-classed Forests. The remaining forests were
declared protected and in these he demarcated a large number of more important areas, including
the majority of old Trihais (closed in 1860) which were termed as Demarcated Protected Forests,
41
while the areas outside his demarcation, came to be known as Un-demarcated Protected Forests.
The Result of Anderson’s Settlement may be summarized as below:
(i) The formation of 138 blocks causing 54802 ha of Demarcated Protected Forests which are
to be maintained permanently as forests (Notification No. 57 dated 26th January, 1897)
amended by Notification No. 991 dated 11th January, 1919).
(ii) Formation of Un-demarcated Protected Forests by application of Chapter IV of I.F.A.
(Notification No. 58 dated. 26th January 1897 amended by Notification No. 992 dated 11th
January, 191.9) to all forests and waste land in which the trees had been declared in
Revenue Settlement record to belong the Govt. except:
(a) The Demarcated Protected Forests,
(b) The Reserved and Un-classed Forests,
(c) Areas in which Deputy Commissioner may from time to time sanction appropriation of
land for cultivation or for any other purpose.
(d) Forest and waste land included in the Jagirs of Rajas of Guler and Dadasiba, Dehra
tehsil.
(iii) The declaration in Notification No. 59 dated 26th January, 1897 (amended vide notification
No. 993 dated 11th January, 1919) of 62 species of trees to be reserved under section 30
(a) of I.F.A. in the Protected Forests.
Table 7: These 62 species are:
S.No. Local Name Botanical Name
1 Chil, Chir Pinus roxburghii
2 Harar Terminalia chebula
3 Dhao or Chat Anogeissus latifolia
4 Kakoran Pistacia integerrima
5 Box Wood Buxus sempervirens
6 Walnut Juglans regia
7 Chest nut Aesculus indica
8 Elm Ulmus wallichiana
9 Khair Acacia catechu
10 Tali or Shisham Dalbergia sissoo
11 Oak Quereus spp.
12 Kiu Diospyros tomentosa
13 Tun Cedrela toona
14 Sal Shorea robusta
15 Bamboo Bambuse Spp
16 Kalam Stemphegyne parvifolia
17 Kandu Diospyros cordifolia
18 Rajain Holoptelia integrifolia
19 Bahera Terminalia belerica
20 Mahwa Bassia latifolia
21 Keor Holarrhona antidysenterica
22 Barna Crataeva religiosa
42
23 Sanan Ougenia dalbergiodes
24 Kamal Mallotus phillipinesis
25 Sarin Albizzia lebbek
26 Jaman Syzygium cuminii
27 Simal Bombax malabaricum
28 Bil Aegle marmelos
29 Kembal Odina wodier
30 Kilawa Wrightia tomentosa
31 Arjan Terminalia arjuna
32 Ber Zizyphus jujuba
33 Asan Tenminalia tomentosa
34 Amla Emblica officinalis
35 Lasora Cordia myxa
36 Patajan Putranjiva roburghii
37 Dhaman Grewia oppositifolia
38 Pariara Erythrina suberosa
39 Ohi Albizzip stipulata
40 Phula Acacia modesta
41 Kikar Acacia Arabica
42 kao Olea cuspidata
43 Karmaru Albizzia odoratissima
44 Kathaman Syzygium jambolana,var.
caryophillifolia
45 Kachnar Bauhinia variegate
45 Maple Acer spp
47 Spruce Picea smythiana
48 Silver fir Abies pindrow
49 Mulberry Morus spp
50 Rhododendron Rhododendron spp
51 Khirk Celtis australis
52 Duri Cedrela serrata
53 Jamun Prunus cerasides
54 Haleo Cornus macrophylla
55 Gui Viburnum nervosum
56 Bado Salix spp
57 Puna Ehretia laevis
58 Badrin Wikstroemia canescence
59 Burj Betula spp
60 Kurumb Machilus spp
61 Doden Sapindus detergens
62 Deodar Cedrus libani var. deodara
(iv) Compilation of a detailed forest record of rights and notification of rules for the exercise and
regulation of these rights.
(v) Notification of rules applicable to the Un-classed Forests under section 76 of I.F.A. 1927
(Notification No. 61 dated 26th January, 1897 amended by No. 994 dated 11th January, 1919).
1.9.6: Gibson’s Forest Settlement for Chhota and Bara Bhanghal (Kothi Kohar and Sawar) (1901-
1903): As these areas are in Palampur Forest Division, hence not being discussed here:
43
1.9.7: Middletion’s Revised Land Revenue Settlement (1913- 1919):
The identification and record of the areas on which the trees were the property the state was the
most important forest matter dealt with in the course of this settlement. In spite of attention to
details which characterized the earlier land revenue settlements, the records were not quite clear
as to the field numbers on which the trees belonged to the Govt. Anderson’s Forest Settlement,
though resulted in a clear record of rights in the Demarcated Protected Forests, did not remove the
difficulty of ascertaining the areas outside the demarcation in which the trees were the property of
the Govt. This verification was carried out by Middleton with the assistance of Mitchell who
prepared tree files by tracing each field number of Lyall’s record and declaring the proprietary
rights of Govt. or otherwise in terms of new field numbers. In doing so the title of the Govt. to
trees in small scattered areas not exceeding 4 acres (4 acre-rules) was generally abandoned. The
Government forests (Ban Sarkar) areas were thus, clearly defined and the matters were brought on
a far more satisfactory footing than ever before and one of the main difficulties of Revenue and
Forest administration was removed.
In the body of the “record-of-rights”, wherever a field number in which the Govt. owns the trees
occur a note to that effect in the remarks column, at the end of the record forming part of the
“ZAMABANDI.” In addition a forest register for each tehsil showing the field numbers and the area
of each tehsil showing the field numbers and the area of each class of forest in every tika was
drawn up.
1.9.8: Mitchell and Walter’s Rotational Closure Scheme (1919):
The forests included in the earlier demarcations and closed to grazing continued to improve but
those outside the demarcation deteriorated steadily and were in the danger of extinction. Realizing
the true state of affairs, the Govt. in order to save the forests from irretrievable damage issued
orders in 1913 for the preparation of a scheme of rotational closure of forests. The I.G.F. who
toured Kangra district in 1915, also suggested to the Govt. that the whole area which was
proposed ever to be closed under I.F.A. should be delimited by a special revenue officer along with
a Forest Officer. Accordingly Mitchell and Walters were deputed for the purpose and their
operations resulted in a scheme known as Mitchell and Walters Rotational Closure Scheme. A
question may be raised as to why a fresh Delimitation of areas to be subjected to Rotational
Closure was felt necessary when already there existed a good number of Demarcated Protected
Forests? It was not possible to consider the then existing Demarcated Forests as the basis for the
new system of “Closure Series” on account of the following 3 main reasons :
(i) The Govt’s right of closure extended equally to both the Demarcated and un-demarcated
Protected Forests and contiguous with the Demarcated Forests there were pieces o Un-
demarcated Forests where there was little objection as to their closure like that of Demarcated
Forests.
(ii) The Demarcated Forests in many cases were large, and included wastes taken from many tikas
and often more than one mauza. The tikabandi of the waste was carried out on the basis of the
grazing ground mainly used by each concerned tika; and though it was rare to find a case in which a
tika grazed exclusively on its own waste and had no mutual arrangement with its neighbours, still it
is obvious that under conditions which render a tikabandi possible, the closure series could not be
very much larger than the waste of each tika.
(iii) The Demarcated Forests included a considerable extent at the forests which could not be
closed without great hardship to the right holders. The best instance is that of the large “chakbans”
which are tikas containing nothing but or very little else than forest and are the property of the
44
whole mauza and not merely of the khewatdars of the nearest cultivated lands. Obviously there
were tracts which conformed to the principles of demarcation in Anderson’s Settlement and they
were, as a rule accepted as Demarcated Protected Forests as they stood. But when the boundaries
had been fixed at Lyall’s Settlement in majority of cases, the tikas bordering chakbans were given
no waste at all, so that their cattle entered direct from the houses into the Demarcated Forests
which contained all the paths from one part of the grazing ground to another and all the watering
places.
In view of the above, the closure series had to be created without reference to old demarcation.
Some Un-demarcated Forests had to be included and some Demarcated Forests had to be
excluded from the new delimitation. Thus for the selection of areas to be subjected to the scheme
of Rotational Closure an amalgamation of the Demarcated and Un-demarcated Forests took place.
The areas so delimited which may be composed entirely of Demarcated Protected Forests or
entirely of un-demarcated Protected Forests or of both, were termed as Delimited Protected
Forests.
There exists some misunderstanding as to the term Delimitation or Delimited Forests. The term
delimitation was used only to avoid any confusion with the previous demarcation. The later
connotes a legal difference between the two classes of forests (Demarcated and Un-demarcated)
while the former is merely an executive act having no legal significance whatever. The Delimited
Protected Forests remained under the charge of Forest Department while some legally
Demarcated Forests excluded from the delimitation, were transferred to the control of the Deputy
Commissioner along with the other remaining forests.
For the forests situated to the left bank of river Beas, In 1927-28 a rotational closure scheme was
framed by Aggarwal and Kundan Singh on the lines of the one for rest of the forests of Kangra
Distt. by M/S Walter and Mitchell in the year 1921. The Punjab Govt. in their letter No. 28863 Fts
approved this on 13th
October,1930. However, this scheme covered only the demarcated protected
forests as in the rest of Kangra District. The scheme recommended closures as under:
Triennial Closure Series1/4th
area of each forest in this series is kept closed for 30 years starting
from 1931-32. Chil forests were allotted to this series. Decennial Closure Series1/4th
area of each
forest in this series is kept closed for a period of 10 years starting from 1931-32. In addition, it was
decided by the Govt. that:
In case of small demarcated trihais of less than 10.12ha. (25acres) extent, the working plan would
not provide for rotational closure but such trihais would remain wholly closed as in past.
Closure in scrub working circle would be for 10 years subject to the reconsideration on the expiry
of that period. Bamboo areas would be closed for 3 months only and in areas actually stocked with
bamboos after gregarious flowering for a period not exceeding 10 years. The scheme was prepared
in a manner so as not to cause the villagers any great inconvenience while assuring the
conservancy of forests. The areas specified in the closure scheme can be closed for management
purposes without any reference to the right holders.
45
1.9.9: Summary of the Results of the Settlement and Schemes (1849 – 1919):
The net result of various measures discussed above was to create the following categories of
forests:
(i) Ban Maufis: which are the absolute properties of the Village Co-proprietary body. No such
forests are found in the tract dealt with i.e. present Dehra FD.
(ii) Reserved Forests: which are the absolute properties of the Govt. practically free from rights of
user, except those admitted;
(iii) Un-Classed Forests: where trees belonged to the Govt. but no closure could be enforced
without the consent of the people.
(iv) Demarcated Protected Forests : (Jungal Mehdooda), where appropriation of land cannot be
granted.
(v) Un-demarcated Protected Forests: (Jungal Gair Mehdooda), where breaking up of land could
be permitted by the Deputy Commissioner.
(vi) Delimited Protected Forests: (Jungal Mehfuza), which were subjected to the scheme of
Rotational Closure and are to be permanently maintained as forests.
1.10: The CO-OPERATIVE FOREST SOCIETIES:
The condition of the Delimited Protected Forests, being under proper management by the Forest
Department improved and was quite satisfactory, but the Un-classed and Un-delimited Protected
Forests suffered badly. Indiscriminate felling, lopping, grazing, browsing etc. resulted in serious loss
of soil cover leading to accelerated soil erosion especially in foot hills. In order to arrest further
deterioration of these forests the Govt. in 1938 decided to associate the villagers in the Forest
Management by entrusting to them the Management of Govt. Forests within each village estate
generally a mauza, provided they agreed to manage the remaining unmanaged forests also under
regular working plans through the agency of Forest Co-operative Societies.
The scheme of the Forest Cooperative Societies was sanctioned by the Govt. vide their letter No.
568-Ft dated 27th February, l940 wherein the detailed administrative aspects of this new
institution were outlined. The detailed organizational set up, the byelaws etc. are given in Vol-II
(Appendix VII) of Rawal Plan for Cooperative Forest Societies (1968-69 to 1982-83) and may be
referred. The scheme was initially sanctioned for a period of 5 years and the first C.F.S. was
registered during 11/1941. The scheme was reviewed and extended from time to time till 31st
March, 1974. Since then efforts have been made off and on to revive the KFCSs and various
meetings and consultations within the Forest Department and the Govt. have been held.
According to figures available, there are no Co-operative Forest Societies in Dada Siba Range.
Dehra Range has the largest forest area under CFS at 2693.99 ha. (2717.05 ha in the previous WP);
followed by Jawalamukhi Range with 728.00 ha under CFS and then Nagrota Surian Range with
127.48 ha under CFSs. The total area in Dehra FD under CFS thus works out to 3549.47 ha.
Table 8: Active JFMCs in Dehra:
Division Range Area Ha Name of CFS Status of CFS
Dehra Jawakmukhi 728.00 24 Gummer Active
25 Muhal Active
Dehra 2693.99 26 Sanot Active
27 Dehra Active
28 Bari Active
29 Paisa Active
30 Tatahan Khurd Active
31 Tripal Active
N-Surian 127.48 32 Haripur Active
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1.10.1: NOTE ON ABOLITION OF PAYMENT OF HAQ-CHUHARAM:
Para 61 of Forest Settlement Report of Kangra, written by Anderson, the Village Community
(Khewatdars) and servants (Rakha, Patwari and Lambardar) had got the provision of payment of
one-fourth share of the gross income from the sale of trees as voluntary grant to be divided among
them. This was not a malikana, paid in recognition of their property in the soil, but was a voluntary
grant made to secure their interest and co-operation in Forest Conservancy.
This Haq-Chuharam system existed in five Forest Divisions of the Himachal Pradesh i.e.
Dharamshala, Dehra, Palampur, Nurpur and Hamirpur falling under the jurisdiction of Kangra and
Hamirpur Districts.
The share of Patwari was scrapped in 1948, when the post of Patwari was declared as a
Government job.
1.11: THE HIMACHAL PRADESH COMMON LANDS (VESTING AND UTILIZATION) ACT, 1974:
With the enactment of the H.P. Village Common Lands (Vesting and Utilization) Act, 1974 the
ownership of soil which was earlier with the village proprietors has vested in the Govt. As a result
of this, the Ban muafi Forests of (Palampur Forest Division) which were the property of villagers
have now become a Govt. property. Similarly, the soil of Un-classed and Protected Forests which
belonged to the people (Govt. having proprietary rights over trees of spontaneous growth or
planted by it) has also vested in the govt. Thus these forests have also become absolute property
of the Govt. subject to the exercise of the rights of users.
1.12: THE FOREST CONSERVATION ACT, 1980:
With the enactment of the Forest Conservation Act, 1980, no forest land can now be diverted for
any non-forestry purpose without the permission of Central Govt. As a consequence, power of
Deputy Commissioner allowing breaking up of land for cultivation in Un-classed and Un-
demarcated Protected Forests has been completely abrogated. Thus the distinction amongst the
Demarcated protected, Un-demarcated Protected and the Un-classed Forests as far as breaking up
of land for cultivation is concerned, has disappeared.
1.13: Legal Position:
1.13.1: In order to have a fair idea of the present legal status of the forests, detailed historical back
ground of the various measures taken in Kangra District as a whole is considered appropriate and is
therefore discussed as under:
1.13.2: Rights and Concessions:
13.3: Protected Forests:
The rights in demarcated protected forests have been clearly recorded in Anderson’s detailed Tika-
wise record of rights. Breaking up of land is prohibited. Deputy Commissioner could earlier permit
the breaking up of land for cultivation. However, this power of the DC has been curtailed under the
provisions of FCA, 1980.
In the delimited protected forest, a summary inquiry into special rights such as right to way, right
to water, likely to be interfered by new delimitation was made by Mitchell and Walters for each
forest and the results are recorded in the forest journals. No detailed record like the one prepared
by Anderson for the demarcated protected forests was attempted. As for the forests formed partly
or wholly of the undemarcated protected forests are concerned, Anderson’s record of rights has
been largely altered and has therefore gone redundant.
47
1.13.3: Un-classed Forests:
Rights in un-classed forests are almost similar to those in the un-demarcated protected forests. No
separate record of rights exists for these forests. The state retains the right of management but
no closure can be effected without the consent of people. There is no prohibition on grazing in
these forests. Earlier there was no statutory provision against breaking up of land for cultivation so
long no damage was caused to the forest growth. However, as mentioned above, the provisions of
FCA, 1980 have now prohibited clearing of land for cultivation in the un-classed forests.Notification
of unclassed is at appendix XVII, XI(a) and XXII of VOL.II
All the rights of users (except those of Gaddis and Gujjars) are appended to cultivated land
assessed to land revenue are acquired or alienated with such land and are exercised only for the
bona fide agricultural and domestic requirements. These are further subject to the condition that
the right holders shall be responsible for the pay of the Rakhas and that the rights will not be
exercised to such an extent that may endanger the very existence of the forest. The Govt. retains
the power to curtail or suspend these rights for sufficient and good reason.
The exercise of rights is regulated by the rules framed under section 32 of I.F.A. vide notification
no. 416 dated 14th August, 1897, amended by no. 55 dated 6th January, 1919 for Kangra.
1.13.4: Rights in Reserved forests:
Right of way and drinking water for the cattle during the hot weather are common in many of the
reserve forests. Right of grazing by Gaddies is well recorded in the settlement applicable in this
division also see appendix X of vol. II
1.13.5: Rights in Protected Forests:
These have been well recorded in forest settlement for DadaSiba Jagir forests where in breaking of
land is prohibited. The grazing rights have undergone a change due to framing of rotational closure
scheme by Aggarwal and Kundan Singh as explained in the fore going paras. Rights of collection of
fuel wood, tree distribution for building purposes and burning of the dead for funeral, marriages
and other agriculture implements have been well defined in the settlement report applicable for
the tract also see appendix XI.
1.13.6: RIGHTS IN UN-CLASSED FORESTS:
The rights in un-classed forests are identical with those of un-demarcated protected forests.
Therefore the enactment of the Forest (Conservation) Act, 1980 there was no prohibition for
appropriation of land, which cannot be now done with the coming in force of the Act. The rules for
preservation, reproduction and disposal of 62 trees reserved vide notification No. 61 dated 26th
January, 1897 and No. 994 dated 11th January, 1919 as given in appendix of Vol. II, apply to these
forests also see appendix XI(a).
All rights of users except those of gaddis are appended to the cultivated land assessed to land
revenue; are acquired and alienated with such land; and are exercised only for bona fide
agricultural and domestic requirements. All rights are granted subject to the condition that the
right holders shall be responsible for the pay of Rakhas and subject to the limitation that right will
not be exercised to an extent which will endanger the existence of the forests. Government retains
the power to limit or suspend rights for sufficient reasons to believe.
48
1.14: Summary of Principal Rights:
The principal rights recognized by the Forest settlement are breaking up of land for cultivation,
timber for building purposes, wood for burning of the dead, funeral rites and for marriage
ceremonies, wood for agricultural implements, grazing, grass cutting, lopping, collection of
medicinal herbs, flowers and fruits etc.
The sale proceeds of grass from the area closed by the Govt. and fruits of trees belong to the
village proprietors. The Govt. is entitled to protect, improve and reproduce the forest growth and
to sell trees to the traders and non-right holder only after meeting the requirement of the right
holders in full.
1.14.1: T.D. RIGHTS IN DEHRA DIVISION:
As per provision of Anderson`s Forest settlement for Kangra District the definition of right-holder is
given under clause 26.27 and 28 which reads as under:
Clause 26: “The first class of right-holders is the proprietary body of the villages and tikas in whose
name the common waste is recorded in proportion to the revenue paid. The proprietors and their
agricultural tenants are presumed to have all the rights admitted within the waste of which they
are co-shares, whether they exercise the rights or not. For any one to come under this class, he
must be the owner of cultivated land assessed to revenue, (b) a share in the common waste must
be appended to that land.If he sells his share in the common waste, retaining his cultivated land
and paying revenue, the purchaser of the waste is not entitled to the forest rights formerly enjoyed
by the seller. He has no rights to trees at zamindari rates, nor lopping of trees, and in short, to any
forest produce. Such a purchaser comes under the second class of right-holders, which consists of
the owners of waste land (un-classed) who pay no revenue. They have been given the same rights
as have been conferred on non-agricultural residents; they may graze their own cattle, cut grass
and collect dry fuel and stones. Under this second class come most of the recent settlers in the
Kangra Valley, who have acquired waste land and laid out tea gardens”.
“The peculiarity of the first two classes of right-holders is that they held the rights not by virtue of
their exercising them, but as an incident of their proprietorship in the land”.
Clause 28: The third class right-holders consist of all-revenue-payers and their tenants who have
been accustomed to exercise rights in the demarcated forests. For this class special record has
been prepared. The test for entry into this is not propriety over the soil but the continuous exercise
of certain customs over the waste included in the forest. Hence it includes not only those who live
and have land in the village and tika in which the waste is situated, but also the people of
neighboring villages over whose waste they have exercised rights. In closing any part of the
demarcated forests the rights of this class must be taken into consideration as provided for”.
Clause 28: “The fourth class consists of those who have rights in the un-demarcated waste. The
test here again is exercise of the rights. No record however, could be prepared and general
definition has been given. Rights in the waste have been allowed to all revenue-payers and their
tenants who have continuously exercised the rights. Under this class, have been included non-
agricultural residents who have been allowed, as an act of grace and on surface, to graze a few
cattle, to collect dry wood and cut grass in the un-demarcated waste. The privileges may be
exercised only for their own domestic requirements”.
As per clause 19 (1) of appendix III of Kangra Valley Settlement by Anderson no trees for building
purposes are admissible at right-holders rate to a person who pay land revenue of less than 8
annas. The relevant clause reads as under.
49
Clause 19: “Trees for building purposes, whether of the priced or un-priced kinds, may be cut only
with the permission of Forest Officer or of any Forest Official specially authorized by him and for
granting trees for these purposes, the Forest Officer will be guided by the following rules viz.
One tree will be allowed for each rupee and part of a rupee being 8 annas or more, of revenue paid
provided that the number of trees granted does not exceed 25, whatever the revenue paid upto
maximum the number of chil should not exceed 10, but in special cases and for cause shown, the
Deputy Commissioner may in his discretion grant a larger number of trees”.
1.14.2: PRESENT POSITION:
The Govt. have decided through Secretary Forests D.O. letter No. Fts (F) 13-30/85 dated 10-12-
1986 read with letter No. 30-53/72 dated 13-03-1987 that persons who have acquired ownership
under Tenancy Act or under the provisions of the Land Reform Act or Govt. scheme of providing
land to the landless will enjoy the concession of getting timber for their bonafide domestic use.
Vide letter No. 30-53/72-SF-IV dated 16-10-89 the Govt. have also decided to grant trees at right-
holders rates to those person also who pay land revenue less than 50 paise (8 annas). Such persons
are entitled for one tree only at right-holder rates for the construction of their houses etc. in
modification of Anderson`s settlement Report for Kangra. These Govt. orders will apply only in case
of persons owning agricultural land. These orders of the Govt. are only applicable in case of
acquisition of agricultural land are and not in case of persons who were allotted land for house
constructions.
From the above it is clear that presently all persons in Kangra District who own agricultural lands
entitled for trees at right-holders rates. However, those who got land for house construction or
who are owners of only wasteland (un-classed) are not entitled to it.
T.D. RIGHTS PROVIDED IN THE SETTLEMENT REPORT OF JAGIR FORESTS OF GULER, DADASIBA,
NADAUN AND KUTLEHAR OF KANGRA DISTRICT (1915): Vide Notification No. 2829-E, the following
rules have been made by the Lieutenant Governor, in the exercise of his powers under Section 31
of the Indian Forest Act, 1878, to regulate the matter with which they deal in respect of the areas
constituted protected forests by Notification No. 2839-A, dated 31st
August, 1915, including the
demarcated protected forests specified in Notification No. 2939-B dated 31st
August, 1915. They
are published under section 77 of the said act.
1. Except where the contrary is stated, these rules apply to the protected forest of both classes.
2. In these rules, unless there is something repugnant in the subject or context. “Record of rights”
means the record prepared in accordance with section 28 of the Indian Forest Act.
“Bartandar” means a person entitled, by virtue of being the owner of cultivated land or of being
the agricultural tenant of such an owner being in possession of special rights, to rights over land or
forest produce, which is the property of another. “Khewatdar” means a person entitled to a right
over waste or forestland by virtue of his sole or joint property in such land. “Right-holders”
includes every person entitled to a right over waste or forestland or forest produce, in whatever
capacity and for whatever reasons exercises that right. “Land assessed to revenue” includes land
which, though liable to assessment, was not charged with revenue at the internal distribution
(bachh) of the last assessment, but has since that assessment been brought under cultivation or
closed with the permission of competent authority.
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XII-(1) The Raja may give permits to bartandars to cut and lop trees required by them for the
following purposes to the extent of their actual requirements
(a) For making fences.
(b) For fuel for marriage feasts.
(c) For fuel for funeral ceremonies, such as mukan, sukha and chawbarak.
(d) For making agricultural and domestic implements.
(e) For making charcoal for the manufacture and repair of agricultural implements.
(f) For the supply of fuel at camping-grounds, but not otherwise for sale or barter.
(g) For making machans.
2. Such trees may only be taken after being marked by a Forest Officer, who will select trees
that may be cut and lopped under this rule to be marked in suitable numbers and in reasonable
convenient localities, but in all cases, crooked, malformed and dry trees and such trees can be
removed in thinning must be marked first. When such trees are not suitable or available, other
trees may be marked but in every case strict regard must be paid, to the interest of forest growth
and regeneration.
3. Chil and bamboo may only be marked and cut or lopped when no other suitable trees are
available, and the Raja shall report to the Deputy Commissioner the grant of all permits to cut or
lop these trees.
XIV- Trees required for building purpose may not be cut except under the permit of the Raja.
XV-(1) Tree for building purpose will not ordinarily be granted often than once in 5 years to any
bartandar, but on special application to the Raja and for special cause shown (e.g. the burning of
the applicant’s house) the Raja may grant trees at shorter interval than 5 years to meet the actual
requirements of a bartandar. The Raja shall report all such grants to the Deputy Commissioner.
(2) Bartandar shall not be refused trees required for the repair of one building merely because
they have received trees within 5 years for the construction or repair of another building.
XVI- Trees given for building purposes must be utilized for the construction or repair of building
within the limits of the village where the cultivated land is situated on account of which the trees
are given unless the contrary has been specially allowed.
XVII- No tree standing within 10 meters of any public road shall be cut without the permission of
the Deputy Commissioner.
XVIII-In case where land revenue has been assessed on the right to timber no permit shall be
granted until such revenue has been paid.
XIX- All permits to bartandars to cut and remove trees (including brush wood) shall remain in
force only for three months from the date of the permit or of the trees being marked under rule XII
whichever is later.
If the trees are not removed from the forest within that period, the permit shall lapse, and
thereafter the trees shall not be cut or removed unless the permit is renewed by the authority that
first granted the trees.
1.14.3: Breaking up of Land for Cultivation: This has been explained in paragraph 10.1 to 10.4
supra.
51
1.14.4: Timber for Building Purpose: For meeting the bonafide requirement of right holder timber
is granted on concessional rate (Zamindari Rate) for the construction or repair of houses, cattle
sheds and agricultural implements. Himachal Pradesh Forests (Timber distribution to Right
Holders) Rules,2010 are at appendixXIX.
Table 9: Rates are mentioned as below:
S N o S p e c i e s R a t e s p e r t r e e o f a l l
d i a . C l a s s e s
1 P i n u s l o n g i f o l i a o f o v e r 0 . 9 m g i r t h 1 . 0 0 p e r t r e e
D a l b e r g i a s i s s o o ( s h i s h a m ) 1 . 0 0 p e r t r e e
D i o s p y r o s t o m e n t o s a ( k i n u ) 1 . 0 0 p e r t r e e
2 C e d r e l a t o o n a ( t u n ) 4 . 0 0 p e r t r e e
3 A n o g e i s s u s l a t i f o l i a ( c h h a l ) 0 . 5 0 p e r t r e e
A c a c i a c a t c h u ( k h a i r ) 0 . 5 0 p e r t r e e
T e r m i n a l i a c h e b u l a ( h a r a r ) 0 . 5 0 p e r t r e e
4 P i s t a c i a i n t e q e r r i m a ( k a k a r s i n g i ) 2 . 0 0 p e r t r e e
5 S h o r e a r o b u s t a ( s a l ) : b a l l i s 1 6 . 5 0 p e r h u n d r e d
P o l l s 5 . 0 0 p e r h u n d r e d
6 B a m b o o s 0 . 2 5 p e r h u n d r e d
7 A l l t h e r e m a i n i n g 0 . 2 5 p e r t r e e
R e s e r v e d s p e c i e s f o u n d i n
T h i s d i v i s i o n a s l i s t e d i n … … s u p r a
The grant of trees to right holders at zamindari rate is normally allowed once in five years & one
tree is given for each rupee of land revenue paid with a minimum 25 trees of which not more than
10 may be chil. Timber is not to be granted if the right holder has got a suitable house in locality
reasonably close to the agriculture holding to which the rights pertain. If the timber is to be used
outside the limit of the village in which it is granted double the rates are to be charged. In special
& unforeseen circumstances such as fire, flood, earthquake etc. the rules may be relaxed.
Number of trees removed for building purpose by the right holders from 1981-82 to 2000-2001:
Table 10: FROM DEMARCATED PROTECTED FORESTS:
R a n g e S p e c i e s N o . o f t r e e s g r a n t e d
V I V I I I I I A I I B I A I B I C T O T A L
D a d a s i b a P i n u s r o x b u r g i i 2 9 5 1 1 7 = 1 6 . 0 3
D a d a s i b a B . L . 2 4 9 5 2 2 2 = 1 4 . 0 3 8
J ’ m u k h i B . L . 5 9 6 2 1 2 3 = 1 6 . 6 7 0
C h i l 3 9 1 2 6 5 3 5 = 5 7 . 0 0
D a d a s i b a C h i l 5 4 3 1 2 = 1 6 . 8 1
J ’ m u k h i C h i l 3 9 1 2 6 5 3 5 = 5 7 . 0 0
D a d a s i b a B . L . 5 1 3 2 1 1 6 4 5 9 = 5 3 . 7 9 6
J ’ m u k h i B . L 5 6 3 1 1 5 = 8 . 6 8 8
D e h r a C h i l 2 1 3 = 2 . 7 4
D e h r a B . L 5 1 9 5 9 4 5 1 7 2 1 3 7 = 1 1 2 . 6 2 7
52
Table 10A: Statement showing the T.D. AND FREE GRANT given to Right Holder from the Year
1996-97 to 2009-2010 from the Left Bank felling series of Chil and other Working Circles.
Left Bank Felling Series 1996-97
Total
W/C F/S PB 10
20
20
30
30-
40
40
50
50
60
60+ No. Vol.
Chil I 1 Chil - - - 12 3 1 16 62.00
3 -do- - - - - - - - -
II 3 -do- - - - 21 5 1 27 46.48
II 4 -do-
Shisham - - - 1 - - 1 0.977
II Other B/L - 4 4 5 2 - 15 11.152
III -do- Chil - - - - - - - -
-do- Shisham - - - - - - - -
-do- B/L - 3 5 9 4 - 21 18.769
Coppice Chil - - 2 5 - - 7 8.50
Shisham - - 8 21 3 - 32 28.82
B/L - - 7 6 - - 13 10.754
Protection Chil - - - 1 1 - 2 4.04
Shisham - - 1 - - - 1 0.467
B/L - 2 9 1 1 - 13 7.84
Plantation Chil - - - - - - - -
Shisham - - - - - - - -
B/L - 4 1 - - - 5 1.69
Left Bank Felling Series 1997-98
Chil W.C. I Chil 1 - 3 - 1 - 5 5.9
Shisham
-
- - - - - - - -
B.L. - 2 3 5 1 - 11 8.97
II Chil - 2 2 51 1 - 64 89.24
Shisham - - - 2 2 - 4 5.00
B.L. - - 1 3 2 - 6 6.62
III Chil - - - - - - - -
Shisham - - - - - - - -
B.L. - - - - - - -
Coppice Chil - - 2 1 6 - 9 18.26
Shisham - - 1 8 7 - 16 18.94
B.L. 1 - 9 13 4 1 28 14.51
Protection Chil - - - 9 1 - 10 15.56
Shisham - - 3 2 - - 5 3.353
B.L. - - - 4 1 - 5 5.86
Plantation Chil - - - - - - - -
Shisham - - - - - - - -
B.L. - - - - - - - -
Left Bank Felling Series 1998-99
Chil I Chil - - 10 19 - - 29 33.86
Shisham - - - - - - - -
B.L. 1 1 - 3 - - 5 1.86
II Chil - - 9 59 - - 68 90.81
Shisham - - - - - - - -
B.L. 3 8 8 - - - 19 23.04
III Chil - - - - - - - -
53
Shisham - - - - - - - -
B.L. - - - - - - - -
Coppice Chil 1 - 33 16 - - 50 43.27
Shisham - - - - - - - -
B.L. - 64 39 1 - - 115 32.53
Protection Chil - - 7 20 3 - 30 36.41
B.L. 2 42 8 2 - - 54 12.77
Shisham - - - - - - - -
Plantation Chil - - - - - - - -
Shisham - - - - - - - -
B.L. - - - - - - - -
Left Bank Felling Series 1999-2000
Chil W.C. I I Chil - - 24 42 1 - 67 78.68
Shisham - - - - - - - -
B.L. - - - - - - - -
II Chil - - - - - - - -
Shisham - - - - - - - -
B.L. 2 2 4 5 - - 13 8.26
Others Chil - - - - - - - -
Shisham - - - - - - - -
B.L. - - - - - - - -
II I Chil - - 29 67 8 - 97 117.93
Shisham - - 3 - - - 3 1.40
B.L. - - - - - - - -
II Chil - - - - - - - -
Shisham - - - - - - - -
B.L. 5 5 19 9 - - 38 21.78
III Chil - - - - - - - -
Shisham - - - - - - - -
B.L. - - - - - - - -
Left Bank Felling Series 2000-2001
Chil W.C. I Chil 3 2 - - - - 5 1.87
Shisham - - - - - - - -
B.L. - - - - - - - -
II Chil 1 - - - - - 1 0.19
Shisham - - - 1 - - 1 0.97
B.L. - - - - - - - -
III Chil - - - - - - - -
Shisham - - - - - - - -
B.L. - - - - - - - -
Protection B.L. 2 11 3 - - - 16 3.30
Plantation Chil - - - 1 - - 1 1.44
Shisham 1 1 - - - - 2 0.64
B.L. 1 1 - - - - 2 0.70
Left Bank Felling Series 2001-02
CSWWC - 1 Chil - - - - 1 - 1 2.60
Coppice - - Shisham - - 1 2 1 - 4 2.633
B.L - 1 5 3 - - 9 7.76
Left Bank Felling Series 2002-03
Chil Others - - 27 4 2 0 33 26.49
Shisham - 1 4 1 - - 6 5.898
B.L - - 6 6 - - 12 12.54
Coppice Chil - - 12 4 1 - 17 16.16
Shisham - - 3 - - - 3 1.401
B.L 10 3 16 3 2 - 34 22.59
54
Protection Chil - - 8 - - - 8 5.99
B.L - 12 3 6 - 1 22 16.41
Left Bank Felling Series 2003-04
Chil Others - - 27 2 - - 29 20.43
Shisham - - - 1 - - 1 0.977
B.L - - 4 2 - - 6 5.48
Coppice Chil - - 17 - - - 17 11.05
Shisham - - 3 3 2 - 8 7.378
B.L 3 9 8 9 2 0 31 25.25
Protection Chil - - 10 - - 1 11 10.04
Shisham - - - 4 3 1 8 10.742
B.L - 38 1 3 - 1 43 13.938
Plantation Shisham - - 1 2 - - 3 4.023
B.L - - - - 2 - 2 5.20
Left Bank Felling Series 2004-05
Chil Others - - 6 - - - 6 3.90
B.L - 2 - - - - 2 0.38
Coppice Chil - - 3 - - - 3 1.95
Shisham - - - 3 - - 3 2.93
B.L - 4 - 1 - - 5 2.20
Protection Chil - - 6 - - - 6 3.90
B.L - 6 - 2 - - 8 1.14
Left Bank Felling Series 2005-06
Chil Others - - - - - - - -
- Shisham - - - - 1 - 1 1.523
B.L - - 2 5 - - 7 8.50
CSW 1 Chil - - - - 1 - 1 2.60
Coppice Shisham - - 1 1 - - 2 1.444
B.L - - 1 6 3 1 11 20.63
Protection Shisham - - - 1 1 - 2 2.50
B.L - - 1 1 2 1 5 10.83
Left Bank Felling Series 2005-06
Chil Others - - 42 1 - - 43 28.75
B.L - 2 2 2 4 - 10 14.96
Coppice Chil - - 16 - 1 - 17 13.00
Shisham - - 3 - - - 3 2.932
B.L - 15 - 2 4 - 21 16.13
Protection Chil - - 5 - - - 5 3.25
B.L - 23 5 7 12 - 47 48.90
Left Bank Felling Series 2006-07
- - - - - - - - - - - -
Left Bank Felling Series 2007-08
- - - - - - - - - - - -
Left Bank Felling Series 2008-09
- - - - - - - - - - - -
Left Bank Felling Series 2009-10
- - -- - - - - - - - - -
55
1.14.5: TIMBER AND WOOD FOR BURNING THE DEAD AND MARRIAGE CEREMONY AND
AGRICULTURAL IMPLEMENTS ETC:
For this purpose the trees have been divided into two categories. 1st category comprising of 62
trees reserved vide Notification No. 59 dated 2-6-1867 as amended vide notification No. 993 dated
11-1-1919. In the 2nd category all other trees of the tract dealt with.
The Lamber-dars were authorized in the past to give permits for cutting of 2nd category trees and
where the 2nd category trees were not available then cutting of crooked and un-sound stumps of
the 1st category of trees with the exception of 19 named trees of 19 species the following species
are found in a tract:
Cedrela toona, Acacia arabica, Celtis australis, Olea cuspidata, Dalbergia sissoo, Shorea robusta,
Pistacia integerima, Terminalia chebula and Terminalia belerica.
The trees must be marked by a forest official before being cut. However, wood of any species
required for burning of the dead, except of 19 named trees may be cut without being first marked
provided that the notice is given to the local forest officials within 10 days. In Dadasiba Jagir, Chil
and Bamboo can only be marked and cut/lopped with the permission of the Divisional Forest
Officer when no other trees are available.
All removal from Dehra Division during the period 2001-2002 to 2009-2010 has been shown at
appendix XXX of VOL. II.
Now the practice of the lambardars granting permission has ceased and trees are cut with the prior
permission of the Forest Department for the purpose except for burning the dead where the
intimation is sent by the villagers after felling.
56
The following statement shows the number of trees granted for
burning of the dead and for marriages
(1986 to 2002)
Table 11: Grants for Marriages and Funeral etc:
R a n g e S p e c i e s V I V I I I I I A I I B I A I B T o t a l V o l m3
D a d a s i b a P r o x b u r g h i i 2 4 3 9 1 1 5 7 8 5 8 . 7 5
N / S u r i a n P r o x b u r g h i i 5 9 1 4 1 5 . 4 9
N / S u r i a n B L 5 3 1 6 7 1 6 1 2 4 2 9 8 2 5 6 . 6 5
3
D a d s i b a P r o x b u r g h i i 1 6 2 9 6 3 3 1 6 1 4 5 1 0 7 . 6 6
D e h r a B L 9 2 6 7 9 7 3 4 1 2 8 6 6 . 2 1 2
J ’ m u k h i C h i l 2 5 5 6 2 0 5 2 3 2 1 6 9 8 6 9 5 8 8 9 . 0 7
D e h r a B L 5 1 5 3 4 1 9 7 3 4 1 . 8 7 5
D a d a s i b a P r o x b u r g h i i 1 1 6 9 2 1 1 2 0 9 6 9 9 3 5 8 1 6 7 3 . 7 6
B L 1 9 6 3 1 3 6 7 6 2 4 3 1 8 2 0 4 . 3 9
D e h r a P r o x b u r g h i i 3 3 5 1 1 5 1 9 2 1 5 3 3 8 2 2 2 . 5 8
B L 2 5 3 5 1 4 8 7 1 9 2 8 8 1 8 1 . 6 4
1
J ’ m u k h i P r o x b u r g h i i 2 5 5 6 2 0 5 2 3 2 1 6 9 8 6 9 5 8 8 9 . 0 1
B L 2 2 4 7 2 8 1 7 6 9 4 4 5 2 6 4 . 3 3
N / S u r i a n P r o x b u r g h i i 5 9 5 9 3 3 1 2 2 . 5 9
B L 1 4 2 9 1 3 1 1 6 3 3 7 3 7 4
57
14.6: Grazing: The right holders may graze any number of animals kept by them for purely domestic
and agriculture purposes. The rules regarding the grazing of sheep and Goats are to be followed
according to the decision of Financial Commissioner that right holders may graze any such animals as
required for their domestic and agricultural (not including pastoral and trade ) purposes, or a number
possessed at O’Brien’s assessment of revenue in 1892, which ever may be greater. The restrictions have,
however, remained a dead letter on account of the impossibility of satisfactorily differentiating between
domestic and industrial, agricultural and pastoral pursuits and of applying O’ Brien’s enumeration
figures which do not distinguish between the gaddi nomadic flocks and the local sheep and goats. Non
agricultural residents can graze their own domestic cattle free if right-holder do not object. All
demarcated protected forests of bamboos of erstwhile Dada-Siba jagir are closed from 15th
Asujie i.e.
from 1st
July to 30 September each year.
1.14.6.1: Gaddi grazing: The gaddis who generally belong to Chamba but in some cases have purchased
land in Kangra to become entitled to all rights of user, are true shepherds. The rich pastures on the
southern slopes of the Dhauladhar provide autumn and summer grazing for four to five months; the
flocks resort to recorded ‘runs’ in the low hills, which afford insufficient and very poor grazing. In the
rainy season the gaddis take shelter behind the main range by moving to Bara Bhangal, Chamba and
Lahaul where very fine grazing is available in the high alpine pastures. The grazing and the movement of
the flocks are governed by the following rules:
(i) Two classes of gaddis have been recognised and pay at present (since 1967) at rates detailed below:
Grazing Fees:
Class In areas where they graze as land owners Recorded Runs
________________(Rs)________________________________________(Rs)_______________
a) Residents Goats 12.50 / hundred Goats 40.00 / hundred
Sheep 4.60 / hundred Sheep 20.00 / hundred
b) Migrants --- -do-
For purposes of enumeration, lambs and kinds born in the spring are counted. Daily stages must be 8 km
apart. No halt ordinarily be made for more than one night at any halting place but when delayed by rain
or by the necessity of giving salt to the flocks, a halt for two nights is allowed. If these limits are
exceeded, a halting fee equal to the full grazing fee is liable but the Deputy Commissioner has discretion
in special cases, to reduce it in case of goats to not less than Rs. 4.69 per hundred. He has ruled that the
halting fee of Rs. 4.69 per 100 should be charged for halting for more than two days but less than six
days unless the halt is for manuring the fields of right holders when no fee is liable; Rs. 6.25 per 100
goats and Rs. 4.69 per hundred sheep, if the stay exclusive of days allowed for manuring exceeds 9 days
but does not exceed 15 days. No flocks are permitted to halt at a place for more than 15 days. The
period of halting for manuring should not exceed 3 nights at one place and halting fee is liable for
excesses even if the halt were for manuring purposes. No halting fee can be charged in tikas where the
gaddis own land and are thus ordinary right-holders provided they confine their grazing to the forests in
which they have rights as owners of land. Gaddis and Zamindars must make their own arrangements in
regard to manuring fields but zamindar may not interfere with gaddis even though they refuse to
manure.
58
1.14.7: Lopping: The rules for lopping have been framed under Notification no. 416 dated 14-8-1897.
Right of lopping is subject to Rules. Lopping of the following species has been prohibited: Toona-
cedrela, Dalbergia sissoo, Shorea robusta, Acacia nilotica, Olea cuspibata, Pistacia integrrima.
Other species may be lopped for fodder, bedding and manure by the right holders and by Gaddis within
their grazing run (For kinds) only provided that no trees less than 50 cm dbh is lopped and branch
exceeding finger thickness should not be cut and trees should not be lopped more than half of their
height and no cutting instruments are to be used and the twigs have to be broken by hand. In the
erstwhile Dadasiba Jagir chil is not to be lopped in any case without the permission of Divisional Forest
Officer. However, B.L. trees may be lopped subject to the afore-mentioned conditions. Natural
regeneration of Annogiessus species has become a problem. To save this species from extinction, no
lopping of this species is allowed till the seeds are shed in the forest.
1.14.8: Zamindari shares: Since 1859 excluding the erstwhile Dadasiba Jagir in the entire tract of the
Division, one third of the sale proceed of the timber and one third income from the sheep/goats grazing
is divided in the ratio of 25%, 37.50%, 25% amongst village proprietors, Lambardars and Rakhas
respectively. The remaining 12.50% was a share of Patwari of the area. This was paid to secure their
interest and co-operation in the forest protection.
The share of the proprietor is paid to the Deputy Commissioner as part payment of the land revenue
demand. Rakhas used get the share directly from the forest department @ 25% of the sale proceed of
timber . However, the payment share is not paid as Malkana in recognition of their property in soil.
1.15: SURVEY AND DEMARCATION:
Un-demarcated protected forests as well as un-classed forests need to be protected against
encroachment. Also to check the boundary of these forests and to avoid any conflict with the local
people it is must that forest land of these forests are well demarcated and boundary pillars erected. The
settlement wing of the forest department with the co-operation of the territorial staff of this area can
do this work with in a period of two to three years provided minimum requirements to carry out such a
task is met with, as follows: Survey & demarcation equipment; Forest survey maps;
Stock maps & any other related records pertaining to particular compartment/forests.
There exists some variation between the forest and revenue entries. This problem can also be solved
and exact forest area can be assigned once for all in case proper survey and demarcation of these
forests is done as per the forest/compartment programme laid down in the appendix VII (a)Vol. II.
1.16: CONSTITUTION OF D.P.Fs:
For proper and scientific management, it is suggested that quite a number of compartments of the
forests of the tract dealt with shows the dire necessity for their proper and scientific management as
new young plantations raised in the past have almost established. The boundaries of these forests be
made intact by proper survey and demarcation and boundary pillars erected. Such forests,
compartments have been recommended to be constituted as demarcated protected forests, in the
concerned compartment history files (also see appendix VIII of Volume-II).
59
CHAPTER - II FLORA & FAUNA
2 A: THE FOREST FLORA:
2.1: Composition and Condition of the Crop:
The forests of the tract are well scattered on both the banks of river Beas. They can be broadly classified
into following groups on the basis of variations which occur due to altitude, edaphic and biotic factors.
a. Scrub forests c. Bamboo forests
b. Chil forests d. Scrub mixed with chil, sal
e. Other Broad Leaved forests
17.1: The forests of this division can be further grouped into various forest types as identified by
Champion and Seth in their book titled, "A Revised survey of the Forest Types of India, 1962".
Group 5: Dry Tropical forests:
i). 5B/C2 Northern dry mixed deciduous forests
ii). 5B/DS1/ Dry deciduous scrub forests.
iii). 5B/E9 Dry bamboo.
Group 9: Sub tropical Pine forests:
i) 9/Cla Lower or Shivalik chir pine forests.
ii) 9/Clb Upper Himalayan chir pine forests.
2.2: Miscellaneous Scrub Forest (Type 5B/C2 & 5/DS1):
These are mainly found between 340 m and 1200 m; that is in the lower areas of the Division, with
average annual rainfall from 600 to 900 mm. These forests occur mainly in Nagrota Surian, Jawalamukhi
and Dehra ranges. The geological formations are mainly conglomerates. Towards the upper limit where
the rocks are generally sandstone, the scrub is replaced by chil.
These forests are composed in varying proportion, mainly of tree/scrubs of Acacia catechu, modesta,
Bauhinia veriegata, Albizzia lebbek, Pistacia integerrima, Lannaea coromendelica, Aegle marmelos, Ficus
relgiosa, Kydia calycina etc. The undergrowth consists of Carrisa opaca, Dodonaea viscosa, Woodfordia
fruticosa, Murraya keonigii, Adhatoda vasica etc. The forests are generally open, degraded and getting
eroded due to overgrazing and excessive exercise of various other rights. The productivity of these
forests is very low. There are frequent blanks presently carrying no vegetation worth the name. Most
species in these forests are of poor utilization and economic value. Regeneration in areas not closed to
grazing is practically absent. The plantations mainly of chil have been raised during the last 15 years by
seeking voluntary closures on favourable sites. The lower areas being very dry and with shallow soils are
difficult to regenerate.
60
2.2.1: TYPE –5B/C2: NOTHERN DRY MIXED DECIDUOUS FORESTS:
This type of forest occurs between altitudes of 340 meter to 900 meter m.s.l. the growth of the crop is
best in deep soil due to retention of moisture contents elsewhere for a major part the upper canopy has
got seriously broken due to various biotic influences. Most part of the tract has been occupied by small
trees and shrubs such as Acacia catechu (Khair), Diospyros montana, Mallotus phillipinensis, Myctanthes
arbortristis, Carissa spinarium and Mimosa rubicaulis and a very little of Shorea robusta. The main
economic species is among them is Khair. Sal is localized in mainly two pockets i.e. Shantla and Saleti.
2.2.2: TREES: Acacia catechu, Anogeissus latifolia, Lannea coromandelica , Aegle marmelos, Mallotus
philippinensis, Flacourtia indica, Limonia acidissima, Ehretia laevis, Zizyphus mauritiana, Ougeinia
ougeinesis, Butea monosperma, Holoptelea integrifolia , Diospyres Montana, Cassia fistula, Mitragyna
parvifolia , Cassia fistula. Casearia elliptica, Bauhinia variegata , Toona ciliata, Albizzia lebbek, Albizzia
odoratissima, Acacia modesta, Acacia nilotica, Acacia leucophloea, Bombox ceiba, Litsea glutinosa,
Eugenia cuminii, Shorea robusta, Emblica officinalis, Erythrina glabresons, Spondias pinnata.
2.2.3: SHRUBS: Carissa spinarum, Mimosa himalayana, Nyctanthes arbortristis, Dodonea viscosa,
Woodfordia floribunda, Adhatoda zeylanica , Murraya koenigii , Zizyphus mauritiana, Holarrhena
antidysentrica, Vitex negundo , Xeromphis spinosa, Lantana camara.
2.2.4: GRASSES: Chysopogon montanus (Dholoo), Hetropogon contortus (Lamboo), Chloris incompleta
(takkevmadhana), Themeda anathera (Lungji), Bothriochloa, pertusa Brachiaria Spp., Eulalispsis binata
(bhabbor), Aristida spp.
2.2.5: CLIMBERS: Pueraria tuberosa, Bauhinia vahlii, Acacia totilis, Clematis gouriana and cuscuta
refleva.
The area under this type is approximately 12000 hectare which is 40% of the forest area.
2.3: TYPE 5B/DSI: DRY DECIDUOUS SCRUB:
Mainly shrubs form the part of this type which usually do not grow beyond 4 meter in height. Continual
over grazing, continuous fire and felling and lopping are said to be responsible for this forest type.
Lantana camera has spread over huge tracts of this type.
The total area under this type is estimated at 8150 Ha, which is 26 % of the total forest area.
2.3.1: FLORISTICS: Dodonaea viscosa, Carissa spinarum wood fordia floribunda, Flacourtia indica
Nyctanthus arbortrists, Lannea coromandilica, Aegle marmelos, Carria fistula, Acacia catechu.
2.4: Chil Forests. (Type 9/cla & 9/clb):
The chil (pinus roxburghii) forests generally occur between elevations of 800 to 1700 on a variety of
formations, the best growth however, is attained between 1200 m and 1700 m on loose sandy loam
soils derived from hard sand stones. Towards its lower limit chil is confined to the cool, northern aspects
while on higher altitudes of about 1200 m and above, it occurs all over preferring ridges. The rainfall
varies from 900 mm to 2600 mm. The site quality of chil is mainly III, the form and growth of the crop is
generally inferior and often exhibits left hand twist.
61
Mohan had classified the chil forests of the composite Kangra Forest Division into three sub types:
(a) Lower or unstable sub-type
(b) Middle or intermediate sub-type
(c) Upper or stable sub type
The forests of lower chil sub type are found between 450 and just over 600 m elevations and are
characterized by a crop of trees of very poor quality, branchy, malformed and often exhibiting very
marked left hand twist. Regeneration of chil both artificial and natural is extremely difficult, and
probably quite frequently impossible. The forests often contain a large proportion of dense scrub where
this is absent; the pure chil crops are very open. Such type is mainly found in Dehra, Dada and partially
in Nagrota Surian Ranges of this Division.
This type covers a total area of 5159.89 hectare which is 16.6% of the total forest area.
The middle of intermediate-sub-type (9/C1a) occurs mainly on Shiwalik conglomerates and sandstones.
This sub-type is mainly confined to some forests of Jawatamukhi, Lapiana and Nagrota Surian ranges.
The common associates of chil in this sub-type are Terminalia chebula, Mallotus phillipinensis, Pyrus
pashia, Syzygium cumin, Albizzia lebbek, A-ordoratissima, Emblic of ficinalis etc. The under growth of
Carissa spinarum, Dodonaea viscosa, Rubus eltipticus, Flacourtia-spp , Murrava Koeniaii is moderately
thick with grass growth of Heteropogon contortus, Themeda anathera, Cymbopogon martinii and
Chrysopogon montana. Naturalregeneration is generally sufficient on cooler/sheltered sites but poor
(almost absent) elsewhere. Fire and grazing are the main factors inhibiting regeneration.
The upper or stable sub-type (9/C1b) occurs mainly between 1200 m to 1700 m and is chiefly found in
Jawalamukhi range. The majority of good chil forests of Dehra and D’sala Divisions belong to this sub-
type. This subtype is characterised by more or less pure crop of chil with a light mixture of Quercus
incana, Rhododendron arboreum, Pyrus pashia, Pieris ovalifolia etc. towards the upper limit and Albizzia
spp, Syzygium, cuminii, Ficus spp, Terminalia chebula, T.Belerica, Bauhinia spp etc. at the lower limits.
The undergrowth of Myrsine africana, Berberis spp, Rubus etlipticus, Murraya Koenigii, Wopdfordia
frutjcose etc. is generally scanty. Natural regeneration is generally profuse and gets established easily if
protection against fire and grazing is ensured. At the upper extremities the occassional fires are,
however, not harmful for chil regeneration as it helps in elimination of other moisture loving broad
leaved species besides making the crop fire resistant for the future.
Such types of forest are found in Jawalamukhi and Nagrota Surian Ranges (Mainly Khaman Block) of this
Division.
This type of forest covers 4300 ha which is 15% of the total forest area of the Division.
2.5: TYPE 5B/E9: DRY BAMBOO BRAKES:
Forest of such types are usually met at an attitude of 340 meters to 850 meters on well drained Shiwalik
formations. Only one species Dandroclamus strictus occurs in the entire tract which forms relatively low
and dense brakes. Congested clumps choked with dry bamboo are a common feature of the entire tract.
However, in the favorable situations of good soil and moisture content, healthy bamboo clumps have
been observed in clusters.
This forest type covers about 500 Ha which is 1.6% of the total forest area of Dehra Division.
62
2.5.1: FLORISTICS: The floristic characteristics are almost the same as that of previous type but the
main associate are as follows:
Diospyros chloroxylon, Holarrhena pubescens , Limonia acidissima, Ehretia laevis , Holoptelea
integrifolia , Erythrina , Anogeissus latifolia, Lannea coromandelica Aegle mermelos, Adhatoda zeylanica
, Carissa spinarum Nyctanthes arbor-tristis , and grasses are very common in the entire area are
Chrysopogon montanus, Chloris incompleta, Themeda anathera.
Gregarious flowering has been reported in the year 1988. Natural regeneration is almost nil. The young
shoots that come out in rains are usually destroyed by over grazing. Broad leaved species except
Malotus phlipinensis also meet the same fate.
Table 12 : Area covered under various forest types:
Type of forest 5B/C2 5B/DSI 5B/E9 9/C1a 9/C1b Total
Area in Ha. 12000 8150 500 5159.89 4300 30109.89
Percent 40 26 2 17 15 100
2.6: GENERAL DESCRIPTION OF THE GROWING STOCK:
As made clear earlier, the main economic species of the area is Acacia catechu (Khair) and the crop is
scattered throughout the tract and is quite dominant in the lower areas of the Division. However, its
growth varies due to many topographic and geological factors; generally it is very good in deep soil as
well in depressions. Sal in the Western limit though showing struggle for survival as found in groups
intermixed with chil and other broad leaved species. Chil is of site quality III. Its growth is comparatively
better on the North or North Eastern aspects. Bamboo clumps which are on the South Eastern side of
Division are found in clusters in Bakarar forest but the growth is stunted and they are disappearing in
Dada Chatwal. Bamboo in Sansarpur Terrace area is almost finished bearing a few stunted group not
more than 2-3 meters in height and replaced by khair which was planted there. Shisham crop is facing
great danger due to drying up; causal organism is yet to be ascertained by the department. Anoguiesus
latifolia is found on the North and North Eastern areas of the Division between 800-1200 meters, in
patches. But its natural regeneration is almost nil due to the factor of over grazing. Terminalias and
Albizia spp., Emblica officinalis do face the same problem due to over grazing and continuous fire,
though their regeneration is satisfactory in the Reserved forests of the division) also see appendix XV for
threatened plants of H.P.
2.7: INJURIES TO WHICH CROP IS LIABLE:
2.7.1: Fire:
Fires are a common feature in Chil forests. Though Chil is greatly fire resistant than any other
Himalayan conifer, yet owing to the fact that is found on hot dry slopes, the actual damage done by fire
in chil forests is very serious . The tree owes its fire resisting power to the exceptionally thick bark
produced alike on young saplings and on older trees, to the thickened and sometimes fleshy tap root
developed in the seedling and young sapling stage, and to the power exhibited in the younger stages
when recovering from injury by means of shoots from collar buds. The trees are though blackened at the
base and the outer back scorched, retain the inner living cortex and the cambium and thus suffer no
permanent injury.
63
The extent of damage caused by fire depends on the condition of the forest and the nature of the soil. It
causes great havoc in regeneration areas and young plantation areas, where young regeneration is
completely wiped out by fires. In even aged crops of above middle age with little or no under growth,
the conflagration is confined to ground and results in retarding the increment and early drying of trees.
In the crops with considerable number of young poles with scattered mature trees or an in irregular
forest with a fair amount of under growth, the damage caused is enormous.
Incendiarism encourages the recession of chil to higher elevations and is certainly one factor in
restricting chil to northern aspects.
It may be emphasized that fires are periodic and not only annual. Pre-disposing causes are accumulation
of dry pine needles, thick under growth, dry grass, felling debris, drought, defective resin tapping etc.
The faulty resin tapping (too close resin channels) is another aggravating cause for the death of the trees
by burning of cambium layer all around the trees. Largely the guidelines for resin tapping are not being
followed and it results in loss of revenue and vitality of trees and their early death. Cause of a
conflagration is not easy to ascertain. Often fires are set on purpose; to obtain fresh grass growth or
drive away wild animals or to encroach upon forest land. Range wise detail of areas Burnt (in ha.)
Table 13: Range –wise Forest Fire Report in respect of Dehra Forest Division: (1997 – 2011)
Year Name of
Divn.
Name of
Range.
No. of
cases
Kind of area affected by
Fire ( in ha)
Total
area ( in
ha)
Estimated
loss ( in
Rs.)
Chil Pine Others 1997 Dehra. Dehra 2 Chil Pine Plantation &
Ground fire etc. 9.00 -
Jawalamukhi 4 -do- -do- 18.50 -
Dadasiba. 2 -do- -do- 20.00 5000
Nagrota-Surian 1 -do- -do- 2.00 -
Total :- 9 - - 49.50 5000
1998 Dehra. Dehra 13 Chil Pine Plantation &
Ground fire etc. 149.50 36300
Jawalamukhi 15 -do- -do- 275.46 100850
Dadasiba. 15 -do- -do- 210.15 200000
Nagrota-Surian 6 -do- -do- 7.75 20500
Total :- 49 - - 642.86 357650
1999 Dehra. Dehra 25 Chil Pine Plantation &
Ground fire etc. 675.50 293152
Jawalamukhi 39 -do- -do- 443.43 438752
Dadasiba. 16 -do- -do- 82.50 215000
Nagrota-Surian 12 -do- -do- 141.50 140233
Total :- 92 - - 1342.93 1087137
2000 Dehra. Dehra 2 Chil Pine Plantation &
Ground fire etc. 14.95 -
Jawalamukhi 3 -do- -do- 7.00 30000
Dadasiba. 2 -do- -do- 2.00 5000
Nagrota-Surian 1 -do- -do- 15.00 3600
64
Total :- 8 - - 38.95 38600
2001 Dehra. Dehra 5 Chil Pine Plantation &
Ground fire etc.. 64.00 58000
Jawalamukhi 3 -do- -do- 38.00 10000
Dadasiba. 5 -do- -do- 20.00 25000
Nagrota-Surian 2 -do- -do- 13.00 57150
Total :- 15 - - 135.25 150150
2002 Dehra. Dehra 25 Chil Pine Plantation &
Ground fire etc. 698.64 668600
Jawalamukhi 25 -do- -do- 347.43 86000
Dadasiba. 26 -do- -do- 380.00 218000
Nagrota-Surian 2 -do- -do- 42.50 19169
Total :- 78 - - 1468.57 991769
2003 Dehra. Dehra - Chil Pine Plantation &
Ground fire etc. - -
Jawalamukhi 51 -do- -do- 728.45 591227
Dadasiba. 7 -do- -do- 13.00 14500
Nagrota-Surian 4 -do- -do- 45.00 60000
Total :- 62 - - 786.45 665727
2004 Dehra. Dehra 15 Chil Pine Plantation &
Ground fire etc. 157.00 297250
Jawalamukhi 1 -do- -do- 13.00 20000
Dadasiba. 5 -do- -do- 25.00 18000
Nagrota-Surian - -do- -do- - -
Total :- 21 - - 195.00 335250
2005 Dehra. Dehra 4 Chil Pine Plantation &
Ground fire etc. 17.00 50000
Jawalamukhi 2 -do- -do- 20.00 23000
Dadasiba. 15 -do- -do- 112.00 240000
Nagrota-Surian - -do- -do- - -
Total :- 21 - - 149.00 313000
2006 Dehra. Dehra 1 Chil Pine Plantation &
Ground fire etc. 29.25 25000
Jawalamukhi 5 -do- -do- 140.00 90000
Dadasiba. 2 -do- -do- 20.00 10000
Nagrota-Surian - -do- -do- - 25000
Total :- 8 - - 189.25 2007 Dehra. Dehra 1 Chil Pine - 3 ha. 25000
Jawalamukhi 1 - Ground fire. 40 ha. -
Dadasiba. 2 Chil Pine - 18 ha. 45000
Nagrota-Surian 2 - Planting area 11 ha. 20000
Total :- 6 - - 72 ha 90000
2008 -do- Dehra 8 Chil Pine Planting area 246.99 ha. 318000
Jawalamukhi 5 -do- - 92 ha. 93000
Dadasiba. 10 -do- - 125 ha. 250000
Nagrota-Surian 2 - Ground fire 15 ha. -
65
Total :- 25 - - 478.99 ha. 661000
2009 -do- Dehra 17 Chil Pine Ground fire 214 285600
Jawalamukhi 9 -do- - 270 250130
Dadasiba. 5 -do- - 75 128000
Nagrota-Surian 4 - Ground Fire 59 51500
Total :- 35 - - 618 715230
2010 -do- Dehra 4 - Forests 72.50 247000
Jawalamukhi 6 Chil Pine - 22.50 72680
Dadasiba. 4 - Others. 41.00 96700
Nagrota-Surian 2 - -do- 16.00 38000
Total :- 16 - - 152.00 454380
2011 -do- Dehra - - - -
Jawalamukhi - - - - -
Dadasiba. 2 - Ground Fire 14.00 8500
Nagrota-Surian 2 - - 1.50 -
Total :- 4 - - 15.50 8500
Non- carrying out of the departmental control burning and other silvicultural operations like pruning,
cleaning and thinning in regeneration & regenerated areas have resulted in wiping out a large number
of successfully regenerated (yet not established) areas. The fires are predominantly ground fires.
I n t h e l i k e l y e v e n t o f r i s i n g a n n u a l t e m p e r a t u r e s d u e t o c l i m a t e c h a n g e , i t i s e x p e c t e d
t h a t d i s e a s e i n c i d e n c e d u e t o v a r i o u s p a t h o g e n s m e n t i o n e d a b o v e w i l l
i n c r e a s e . I t i s t h e r e f o r e e s s e n t i a l t h a t a n e f f e c t i v e m o n i t o r i n g p r o t o c o l f o r
e a r l y d e t e c t i o n o f f o r e s t d i s e a s e s i s p u t i n p l a c e , p e r h a p s t h r o u g h a l o n g
t e r m m o n i t o r i n g a r r a n g e m e n t w i t h t h e H F R I , S h i m l a . A p p r o p r i a t e
p r e v e n t i v e a c t i o n a s r e c o m m e n d e d b y s c i e n t i s t s , n e e d s t o b e t a k e n u p b y
t h e d e p a r t m e n t a n d c a n b e f u n d e d u n d e r N P V c o m p o n e n t o f C A M P A .
2 . 8 : F A U L T Y R E S I N T A P P I N G & C O N S E Q U E N C E S :
T h e r e i s a b i g p r o b l e m w i t h r e s i n t a p p i n g . I n C h i l f o r e s t s f a u l t y r e s i n t a p p i n g i s
p e r h a p s t h e b i g g e s t t h r e a t t o t h e f o r e s t s . T h e R I L L m e t h o d w a s i n t r o d u c e d
s e v e r a l y e a r s a g o . T h i s i s s u p p o s e d t o b e l e s s d a m a g i n g t o t h e t r e e i f
p r o p e r l y c a r r i e d o u t . H o w e v e r , i n s p e c t i o n o f t h e C h i l f o r e s t s s h o w s t h a t
n e i t h e r t h e C o r p o r a t i o n s t a f f o r t h e F o r e s t s t a f f o r t h e R e s i n l a b o u r o f t h e
C o n t r a c t o r h a s b e e n t r a i n e d o r h a v e a c l u e o f w h a t t h e R i l l m e t h o d
e n t a i l s . R e s i n i s p r o f i t a b l e b u s i n e s s f o r t h e C o r p o r a t i o n w h i c h h a s a
v e s t e d i n t e r e s t i n m a x i m i z i n g y i e l d a n d i n t h i s p u r s u i t t h e c h i l t r e e s a r e
v i r t u a l l y b e i n g t a p p e d t o d e a t h , w h e r e a s t h e R i l l m e t h o d w a s i n t r o d u c e d
t o p r e c i s e l y o v e r c o m e t h i s p r o b l e m . I n f a c t t h e r e i s a n i n c e n t i v e f o r t h e
c o n t r a c t o r t o m a x i m i z e r e s i n y i e l d p e r s e c t i o n a s t h e C o r p o r a t i o n p a y s f o r
r e s i n e x t r a c t e d e v e n w h e n a l i m i t o f 3 0 q u i n t a l s p e r s e c t i o n h a s b e e n
f i x e d a s t h e m a x i m u m p e r m i s s i b l e y i e l d . T h e r e i s v i r t u a l l y n o c h e c k i n g b y
t h e f o r e s t s t a f f a n d d a m a g e b i l l s m a d e a t t h e e n d o f t h e s e a s o n a r e m o r e
f o r t o k e n i s m t h a n t o e f f e c t i v e l y c h e c k / d i s c o u r a g e f a u l t y t a p p i n g ( a l s o
s e e a p p e n d i x - X V I I I f o r H P R e s i n a n d R e s i n p r o d u c t s R u l e s - 2 0 0 2 ) .
66
T h e r e s u l t i s t h a t t h e C h i l f o r e s t s a r e d y i n g . B a d t a p p i n g v i r t u a l l y g i r d l e s
t h e t r e e a n d r e p e a t e d f i r e s s o w e a k e n t h e s t e m t h a t s o o n e r t h a n l a t e r t h e
t r e e f a l l s d u e t o w i n d o r i n s t o r m s . B e i n g a g o v e r n m e n t c o r p o r a t i o n
m a n n e d b y f o r e s t o f f i c e r s o n d e p u t a t i o n , i t i s d i f f i c u l t / t r i c k y t o t a k e
p e n a l a c t i o n a g a i n s t w h a t a r e s e e n a s f e l l o w o f f i c e r s / o f f i c i a l s . T h e r e i s
n o i n c e n t i v e t o d i r e c t s t a k e h o l d e r s t o t h i n k o f s u s t a i n a b l e t a p p i n g . T h e
C o r p o r a t i o n s t a n d s t o m a k e m o r e m o n e y i f i t p r o p e r l y f o l l o w s t h e R i l l
m e t h o d b y w a y o f m a n y m o r e y e a r s o f t a p p i n g t h e s a m e t r e e . O t h e r
i r r e g u l a r i t i e s l i k e i l l i c i t t a p p i n g m a k e t h e s c e n a r i o w o r s e .
I t i s c l e a r t h a t m a n y a r e a s l i k e P B I s h o u l d n o t b e a l l o w e d t o b e t a p p e d
a n d o v e r t a p p e d a r e a s s h o u l d b e g i v e n c o m p l e t e r e s t f o r t h e
p e r i o d o f t h i s W o r k i n g P l a n .
T a b l e 1 3 :
B l a z e s o n p r i v a t e t r e e s i n D e h r a F D B l a z e s i n G o v t f o r e s t s h a n d e d o v e r t o
H P S F D C
Year No. of Blazes Year No. of Blazes
2001 29160 2001 24046
2002 37867 2002 50855
2003 59871 2003 48671
2004 65378 2004 49096
2005 71323 2005 47544
2006 80731 2006 58500
2007 70230 2007 59909
2008 75470 2008 58439
2009 73437 2009 55779
2010 69541 2010 56839
2011 76635 2011 75578
2.9: CLIMATE:
Climate plays an important role in regeneration of forests. If all conditions relating to climate are
favorable they directly contribute to the growth of plants. Sometimes the conditions vary and do
considerable damage to growth as well as survival of regeneration which results in permanent loss of
vegetation with gaps in the canopy and this leads to openings that make way for entry of weeds,
unpalatable grasses and so forth.
2.9.1: Climate Changes:
As a general trend, temperatures, especially in summer, have been rising throughout the tract. People
report that it is now less cold during peak winter. However, there does not appear to be any great
variation in annual rainfall figures over the last couple of decades. What does appear to be happening is
that there are now more extreme rainfall events leading to local flooding and consequently to more
erosion. The Chil and other BL forests with thick, dry undergrowth of Lantana during summer are more
vulnerable to fire outbreak and spread potentially causing much more damage to standing trees than
heretofore. This is especially true for established plantations of khair.
67
2.10: DROUGHT:
As the entire tract is rain fed, delay in the monsoon means drought in the area. This not only affects the
germination of forest seeds but also makes the conditions ideal for fire to destroy the vegetation right
from the seedling to the pole stages. The rainfall pattern shows two distinct dry seasons, April, May,
June and October, November and in the last few decades December too. Thus nearly half of the year is
rainfall deficient and low water retention capacity in the forests – due to their continual degradation –
leads to drought like conditions frequently. On the other hand, heavy to very heavy rainfall events
causing “flash floods” are reportedly becoming more frequent and erratic. Such events even once a year
cause heavy damage to forests, plantations and of course severe erosion.
One way of tackling drought like situations is to go in for large scale staggered contour trenches
especially in degraded and erosion prone hill sides. Such initiatives have been taken up under MNREGA
in the department during the last few years and given the availability of MNREGA funds. This could be
replicated on a large scale in nearly all the forest beats of Dehra FD. Another advantage is that staggered
contour trenching could be taken up simultaneously in areas where lantana is being tackled and bamboo
can be planted in the trenches for better survival.
2.11: EROSION:
The entire tract is rain fed and fragile. Sudden increase in down pour further aggravates depletion of
vegetative cover and makes way for weeds to come. Continuous fire and over grazing, illicit lopping and
illicit felling makes the situation ideal for erosion. Top forest soil is lost, and sand stones are exposed.
Finger like projections are quite apparent due to such erosion and are available mainly in Dadasiba,
Dehra (Bankhandi block) and Nagrota Surian Ranges (Baldoa forest).
2.12: WIND:
Wind causes considerable damage to chil forests. Badly tapped chil trees immediately fall victim to wind
and as a result, get uprooted. While falling and sliding down the hill such trees damage the nearby
saplings and makes it easy way for fire to engulf the area.
2.13: LOPPING:
Generally done for procuring fodder, twigs for fuel wood and spreading leaves under the domestic cattle
to protect them against moisture created by animal excreta which later on after dumping becomes a
source of manure for agricultural fields. Lopping is not restricted to the vicinity of villages but has found
its way deep into the forests even reserved forests are not spared. At certain locations Pinus roxburghi,
Acacia catechu, Terminalia tomentosa, Albizzia lebek are victim of such human activities which affects
seed production and trees cannot develop proper canopy. Anogiessus latifolia is the worst affected
species. Its lopping is done before the seeds mature and this further reduces the chances of natural
regeneration. If at all they get little chance grazing does not allow it to grow. Lopping impact of this
species is severe in Nagrota Surian Range (Amblela, Baldoa forests) and Jawalamukhi Range of this
Division.
Table 13: Illicit lopping
Year No illicit
lopping
cases
Amt of
compensation
Rs:
Year No illicit
lopping
cases
Amt of
compensation
Rs:
1995-96 418 11015 2003-04 180 11523
1996-97 470 15246 2004-05 185 9257
1997-98 284 10254 2005-06 116 5915
68
1998-99 286 10781 2006-07 100 4730
1999-2000 35 1460 2007-08 79 20936
2000-01 927 38857 2008-09 249 17513
2001-02 125 5630 2009-10 122 7748
2002-03 208 10830
2.14: GRASS CUTTING:
Illegal grass cutting as well as cutting grass and bamboo without the supervision of forest functionaries
has done considerable damage by cutting the planted and naturally regenerated seedlings along with
the grass. At certain places grass is cut before it sheds its seed. Thus germination process is stopped and
makes the situation ideal for erosion or for unpalatable grasses to come up.
2.15: MARKING AND FELLING:
Trees are generally marked for felling by Right Holder and Forest Corporation. At the time of marking
interest of the individual is given top priority than of the forest; as a result a good seed bearer with clear
bole and well spread crown is axed. Furthermore, avoidable and unavoidable damage causes a great set
back to the growth of the vegetation. The situation becomes worse when debris is left in the forests,
aggravating fire hazard.
2 . 1 6 : I N S E C T S A N D F U N G I :
An insect like Hypophyla robusta , a chil borer, has caused some damage to chil forest in the area.
Termites have caused tremendous damage to shisham seedlings as well as plants of many broadleaved
species up to the sapling stage. If unchecked, it will cause havoc to the entire tract of the scrub forest.
Bugworms (clemia crameri), caterpillers appear occasionally locally in the chil forests and cause
defoliation. However, the damage has not been much.
Locusts (Acridium peregrnum) swarmed the areas of the tract in 1935, 1938, 1950, 1951 and 1955. The
damage was serious in the years 1950 and 1955. Thereafter, it has not appeared. This causes mortality
among bamboo and chil trees and increment to be put on by the forest for a year or two is lost as it
strips the plants naked of all leaves.
A fungus (Ganoderma-lucidium and fusariam) has been reportedly responsible for the drying up of
shisham crop. Large numbers of trees of shisham have dried up in the last two years since the
appearance above named fungus in the area during the year 1999 to 2000 .The process of drying has not
stopped and is still continuing in the entire tract. As no remedial measures have been taken by the
departmental agencies though suggestions in this regard were made by the H.F.R.I. Shimla and F.R.I.
Dehradun. These need to be implemented as so far nothing appears to have been done in the field in
this regard. As a result the drying up of the Shisham has been continuing. It will be a parmanent loss to
this species and it will create a permanent gap in the growing stock and create difficulties in re-
establishing shisham crop in the near future.
2.17: CLIMBERS:
Not much damage by climbers has been done in the area. However, some damage caused by Bauhinia
vahlii in bamboo forest of Santla Beat and scrub forest in Saleti beat of Dehra Range by hampering the
growth of the plants and shoots in the earlier stage has been seen.
2.18: ALIEN INVASIVE SPECIES:
Much damage to the forest has been caused by Lantana camara in the entire tract of the area dealt
with. Especially damage caused by it is much severe in the dry mixed deciduous forest and dry
69
deciduous scrub forest. Continuous fire, illicit grazing and grazing beyond the carrying capacity of the
area and browsing and lopping create the openings and paves way for the entry of Lantana camara.
Other weeds namely, Murraya, Carissa are also commonly found in the area.
Table 14: below shows the results of a survey carried out to assess the spread of Lantana in Dehra FD in
early 2010:
Range No of Forests
Surveyed Total Forest
Area covered Approx. Area in Ha
Under Lantana Percentage
Jawalamukhi 10 1249 1008 80.70
N/ Surian 8 2477 1010 40.77
Dada Siba 28 3559 2168 60.91
Dehra 119 7461 4821 64.61
165 14746 9007 61.08
Out of the 165 forests surveyed, it turns out that over 60 % of the area is already infested with lantana.
Range wise the infestation varies between 61 % in Dada Siba to over 80 % in Jawalamukhi. This position
is alarming and given the very high pressure of grazing in the division, (see next section), there is little
hope of any natural regeneration of native species coming up. Even existing plantations done in the last
few years would be susceptible to suppression by lantana. Clearly then, any strategy aimed at
regenerating the forests of Dehra FD during the course of this Working Plan would primarily need to
tackle the spread and elimination of lantana as a top priority. A tested and good method for the
eradication of lantana has been discussed in Protection cum rehabilitation Working Circle chapter of
part II of this Working Plan.
2.19: GRAZING:
Grazing by domestic animals and that too in the area not open for grazing or grazing in the area open for
grazing beyond the carrying capacity and grazing by stray cattle called Bhutars has caused tremendous
damage to the natural regeneration as well as to the plantations raised artificially. The damage of this
kind has been seen more in scrub forests. In Bankhandi area 2-3 years seedlings of Dalbergia sisso had
been found browsed so severely that its growth is still at ground level and give it a stunted look, (merely
2”-3” at ground level). Overgrazing has caused a great damage to the economical species of the area and
has opened door for the weeds to enter in.
Table 15: The latest Cattle Census Figures for Dehra FD are:
Range Mules Cows Ox Buffaloes Goat Sheep Horse Total
Dehra 499 8584 5572 13237 4473 920 133 33418
N / Surian 535 9525 4573 10235 3575 725 335 29503
Jawalamukhi 395 8120 5520 12645 4590 825 110 32205
Dada Siba 330 6692 4561 12620 4013 860 65 29141
124267
(Source: Vet Deptt. 2007)
Table 16: Grazing Permits issued to Migratory Graziers in Dehra FD:
Years Name of
Range
Number of grazing
permit issued to
Gaddis
No. of
Sheep
No. of
Goat
Total
2001-02 to 2010-11 N / Surian 171 13061 5559 18620
70
2001-02 to 2010-11 J/mukhi 207 20584 5185 25769
2001-02 to 2010-11 Dada Siba 49 6201 3320 9521
2001-02 to 2010-11 Dehra 45 5664 3114 8778
Totals 472 45530 17178 62708
2.20: ENCROACHMENTS: Of the total forest area of Dehra division, about 81% falls in the categories of
Un-demarcated PF, Un-classed forests and Co-operative Societies forests. All these forest categories are
not demarcated or surveyed on the ground thus making them highly vulnerable to encroachments. In
order to ensure proper protection of the forest estate and to prevent further encroachments it is
imperative that all the fore mentioned categories of forests need to be properly surveyed and
demarcated using GPS and permanent boundary pillars within the period of this Working Plan.
Table 17: DETAILs OF ENCROACHMENTS CASES YEARWISE/ RANGEWISE W.E.F. 2006-07 TO 31.03.2011
Year Name of
Range
Encroachment
cases pending
Cases decided
by Collector-
cum-DFO
Cases sent
back to the
revenue court
Cases
evicted
Appeal filed in the
court of Divisional
Commissioner
2006-07 Dehra 19 19 0 11 8
Jawala Mukhi 36 36 0 27 9
Dadasiba 2 2 0 2 0
Nagrota Surian 0 0 0 0 0
Total 57 57 0 40 17
2007-08 Dehra 11 9 1 5 4
Jawala Mukhi 0 0 0 0 0
Dadasiba 0 0 0 0 0
Nagrota Surian 0 0 0 0 0
Total 11 9 1 5 4
2008-09 Dehra 3 3 0 1 2
Jawala Mukhi 0 0 0 0 0
Dadasiba 0 0 0 0 0
Nagrota Surian 0 0 0 0 0
Total 3 3 0 1 2
2009-10 Dehra 1 1 0 0 1
Jawala Mukhi 2 2 0 0 2
Dadasiba 2 2 0 2 0
Nagrota Surian 0 0 0 0 0
Total 5 5 0 2 3
2010-11 Dehra 3 3 0 3 0
Jawala Mukhi 0 0 0 0 0
Dadasiba 12 12 0 2 0
Nagrota Surian 0 0 0 0 0
Total 15 15 0 5 0
71
Table 18: Boundary Pillars in Dehra Forest Division:
Name of Range. No. of Boundary Pillars. Total
Small Large.
1 2 3 4
Dehra 523 206 729
Nagrota- Surian 369 327 696
Dadasiba 508 168 676
Jawalamukhi 443 217 660
Grand Total 1843 918 2761
II(B) FOREST FAUNA
20: The Dehra Forest Division surrounds the Pong Reservoir which is also a Wildlife Sanctuary, a Ramsar
site and now an internationally known destination for wintering migratory birds in north India. The
birds of Pong have been recorded quite well in “BIRDS OF KANGRA” . A more recent, illustrated book
“WILD WINGS “ on the birds of Pong as well as on the fauna of the area including butterflies has been
brought out by Sh. Devindra Dhadwal, Forest Range Officer who has spent over 5 years in the Pong area
documenting and researching local and migratory birds of the Pong wetland.
The Wildlife Wing of the HP Forest Department has launched a dedicated website for the Pong wildlife
sanctuary at:
www.hpkangra.nic.in/pong
2.20.1: Table 19: Human Leopard Conflict cases / incidents reported from Dehra FD:
S No Year Range Particulars Remarks
1 2002-03 DADA SIBA Leopard kill 1 Jersy cow Compensation granted
2 2003-04 Jawalamukhi Leopard injured lady Compensation granted
3 2003-04 Dehra Hunted by hunter This leopard was declared man eater.
4 2003-04 Dada Siba Leopard kills 8 goats & 1
jersey cow
Compensation granted
5 2004-05 Dehra Trapped Rescued and was sent to Gopalpur
zoo.
6 2004-05 Dehra Illicit poaching FIR registered with police; later
Offender reported untraceable.
7 2004-05 Nagrota
Surian
Illicit poaching FIR registered with police; later
Offender reported untraceable.
8 2005 Jawalamukhi Leopard injured human Compensation granted.
9 2007 Jawalamukhi Leopard injured human Compensation granted.
10 2007-08 Dehra Illicit poaching FIR registered with police; later
Offender reported untraceable.
11 2007-08 Dada Siba Leopard kill 1 Jersy cow Compensation granted
12 2010 Jawalamukhi Leopard injured human Compensation granted.
72
2.20.2: Monkey Problem Areas in Dehra FD: People have not totally abandoned cropping, but, there
are cases where some farmers are abandoning cropping in the outer periphery of the villages, esp. in
areas which are less productive. Areas like Bilaspur (Bilaspur beat,Range-Nagrota), Jhakleharh (Maeoa
beat,Range-Dehra ), Dargeh (Sakari beat,Range Nagrota Surian), Jalakh (Beat-Bilaspur,Range-Nagrota),
Guler(Beat-Bilaspur,Range-Nagrota) etc.
Table 20: Approximate number of monkeys from / around temples in the Division:
Range Beat Areas Approx Numbers
Dehra Bankhandi Bagla Mukhi Temple 250
Dehra Shantla Nihari 20, Do not stay permanently
Dehra Kurna Saleti 20, -do-
Nagrota Surian Masrur Masrur Temple 100, incl. surrounds
Nagrota Surian Haripur Ram mandir 100
Nagrota Surian Haripur Santoshi Mata Mandir 150
Nagrota Surian Guler Guler Railway station 180
The above numbers, however, do not reflect a dire, agriculture threatening scenario.
2.20.3: Table 21: DETAILS OF VULTURE NESTING SITES IN DEHRA FOREST DIVISION;
Recorded in 2010-11:
(Source: Range Officer, Wildlife, Nagrota Surian)
The alarming decline in vulture populations across the country due to the widespread use of diclofenac (
a now banned drug), has become an area of concern prompting documentation of vulture breeding sites
and initiating conservation action like prevention of forest fires around these sites, as a matter of
urgency. The forest department & Corporation staff needs to be made aware of this priority and
constantly monitor the status of vulture breeding sites in their areas.
The names of the local and migratory birds and wild life found in the area has been mentioned in the list
of common animals and birds of Vol-1 part -I.
S N NAME OF
PLACE
NAME OF
BEAT
NAME OF RANGE Co-Ordinates NAME OF BREEDING
LOCATION
1 Surani Surani Jawalamukhi U-5D Ghandwar
2
Bateharh Khuman Nagrota-Surian
N 32,13.5725,
E-76,0.8555 U-2D Ladol
3 Lalpura Masroor Nagrota-Surian N 32,4.8405,
E-76,8.6815
R-27D Khuman,
U-11D Jani Masroor
73
74
CHAPTER - III
UTILIZATION OF FOREST PRODUCE
3: AGRICULTURAL CUSTOMS AND WANTS OF THE PEOPLE:
3.1: POPULATION: The population density for Kangra district is 263 persons / sq. km as against the
state average of 123 persons / sq. km., (Census, 2011). The corresponding figures for Dehra FD are 237.5
/ sq. km in 2001 and 300 / sq. km in 2011. Given that about 75 % of the 1200 sq.km area of Dehra FD is
under non forest use, agriculture remains the pre-dominant economic activity. The operational land
holding for Kangra district is recorded as 0.90 ha (Director, Land Records, 2000-01). Assuming a similar
figure as applicable to Dehra FD, it is clear that the average size of land holding is inadequate to provide
sufficient food grains for a family of five for the entire year. Therefore, dependence on waged labour is
very high. With an average sex ratio of over 1000 in all the tehsils of Dehra FD (Census 2001), it appears
that a large number of males work outside the area and, many reportedly in the army.
Generally most of the population works on daily wages with P.W.D., I.P.H., Forest, and HPSFC. Main
economic species of the area is khair. Khair which grows on private land is allowed to be felled under the
10 year felling programme and regulated under L.P.A. and I.F.A. The grower gets remunerative prices by
selling their khair trees which are used to make its product ‘katha’ in bhatties established in this division
and some of the khair wood is also sold to Sagar Katha Udhog at Kala Amb in Sirmour District and
Mahesh Udyog at Gagret.
Resin extracted from chil is another source of income for the local people. Fuelwood extraction and
bamboo clumps add to the income of local people. Since the entire tract dealt with is rainfed barring
300, hactare agricultural land which has been brought under irrigated land. Accordingly people grow
rice, wheat and maize. A very few of the farmers are able to produce surplus which they send to various
adjoining markets, otherwise almost all produce is used to meet their own requirement. The food
grain,pulses, salt are generally imported from the adjoining areas of Punjab state.
The rural population greatly depend on forests, mainly for timber, fuelwood charcoal, wood for
agriculture implements, grass and fodder for live stock, leaves for manure, stone and slate for building
works and herbs for medicinal use etc., as per their rights recorded in the forest settlement. Pressure on
forest is, therefore, tremendous. The rural population depends much more on timber for construction of
their houses, than the urban population as the latter has started using iron door, shutters, window
frames. Gradually with the influx of money due to various employment resources and forestry based
revenue generating resources, the income of rural population has increased considerably and is
gradually switching to pacca houses. The pressure is not on chil species but much on shisham, toon and
other broad leaved which are preferred to chil because latter is attacked by termites. Annual
requirement of timber for building purpose is about 260 m3. The rural population depends on forest to
meet fuel wood requirement. A very few are having L.P.G. connection which is supplied by one Agency
at Dehra. Recently in the beginningof year 2001 one more LPG Agency has been opened at Jawalaji. The
urban population generally use LPG gas to meet there energy requirements. Even the hoteliers and
dhaba owners have started switching on LPG to a greater extent. Apart from the above the pressure for
the requirement of fuel wood in the rural areas for coal tarring of roads by PWD still exists. Grazing
remains a great burden on the forests, not only the local cattle but the migratory sheep & goats of
gaddis graze in the area under due permit obtained from the Division Office at Dehra.
75
It has been observed that grazing has become a great nuisance to the forest especially for young
regenerating coppice shoots, natural and artificially raised seedlings which ultimately makes the area
vulnerable to fire and erosion and opening caused due to plucking of the leaves for fodder by means of
lopping, make entry of weeds.
3.2: MARKET AND MARKETABLE PRODUCTS:
Chief marketable forests products are: 1. Resin 2. Bamboo; 3. Chil timber and pulp wood; 4. Katha
5. Charcoal and fire wood
3.2.1: RESIN: Resin is being extracted through H.P. state forests corporation every year. Following table
reveals the resin extracted by HPSFC and Private resin received from the land holding of people. Table
11(b) shows yearwise resin blazes worked in Govt. and private lots.
3.2.2: BAMBOO: Bamboo is being extracted by HPSFC from Govt. forests and by individuals from
private areas. The following table depicts the quantum of bamboo extracted from the division.
Table-22: Detail of Bamboos and Resin Extracted in Dehra Forest Division during last 17 years:
Year Bamboo (in Nos) Resin Blazes
Govt. lots Private Govt. Lots Private
1993-94 20436 ____ ____ ____
1994-95 47964 ____ 41301 ____
1995-96 ____ ____ 36721 ____
1996-97 ____ 121491 23206 49995
1997-98 147105 188666 25155 47081
1998-99 67972 105056 26972 43893
1999-2K ____ 155404 21827 30999
2000-01 ____ 245931 24317 32067
2001-02 14870 264280 50855 29160
2002-03 6020 206792 48671 37867
2003-04 8390 236509 49096 59871
2004-05 5808 234403 47544 65378
2005-06 0 241860 58500 71323
2006-07 44508 343630 59909 80731
2007-08 0 0 58439 75470
2008-09 0 0 32529 79074
2009-10 0 834612 56839 69541
3.2.3: CHIL TIMBER AND PULP WOOD:
Chil is an important species of the area. The timber is used for railway sleepers and for making pulp. The
table depicts the chil timber and pulp wood taken out of the forest. ???
3.2.4: KATHA:
Katha is derived from khair wood. There is complete moratorium on green felling. However, katha is
being obtained from Private forests via the 10 year felling cycle regulated under the LPA. As on 3/2001
76
there were 6 Katha Bhatties in this division. Part of khair wood is sold to Mahesh Udyog at Gagret and
Sagar Katha Udyog at Kala Amb, Sirmour District in H.P.
Katha:
The following table depicts the quantity of Katha exported from this division in last 18 years.
Table – 23: Katha exported
Year Qty in qtls Year Qty in qtls
1993-1994 941.50 2002-2003 1076.00
1994-1995 390.03 2003-2004 923.00
1995-1996 895.85 2004-2005 628.00
1996-1997 938.76 2005-2006 744.00
1997-1998 981.70 2006-2007 768.00
1998-1999 651.10 2007-2008 1008.00
1999-2000 837.25 2008-2009 650.00
2000-2001 1133.65 2009-2010 658.00
2001-2002 1125.00 2010-2011 673.00
Total 15022.84
3.2.5: FIRE WOOD AND CHARCOAL:
There being a complete ban on green felling, fire wood and charcoal is generally extracted from the
salvage trees marked for the HPSFDC. In addition, private areas also contribute to fire wood and
charcoal extraction.
3.3: LINES OF EXPORT:
Main line of export is the roads as almost entire tract has a network of Kacha & Pacca roads. Labour for
the conversion of charcoal is generally local where as it is imported from Nepal & J&K for timber
extraction & khair wood extraction right from felling to its transportation to road side.
3.4: PAST AND CURRENT PRICES:
Market reflects upward trend due to increase in demand of forest produce. It is elucidated in the
following table; -
Table – 24: Statement showing the per/M3 cost of various forest produce as mentioned under from the
year 1996-97 to 2009-2010 in Fatehpur forest working division.
Year Timber
P/M3
Fuel wood
P/M3
Charcoal
P/Qtls
Khair wood
P/M3
BL Logs
P/M3
Bamboo
P/Bundle
Resin
P/Qtl
1996-97 3693 164 182 8198 8704 48 1932
1997-98 4257 212 215 6756 6868 56 2203
1998-99 5621 216 266 8141 7828 56 2610
1999-2K 6249 230 191 9984 8243 62 1567
2000-01 6050 263 188 9653 7495 96 2651
2001-02 3200 800 600 20000 2300 0 2300
2002-03 3200 800 600 20000 2200 0 2400
2003-04 3200 800 600 20000 2500 60 2200
2004-05 3200 800 600 20000 2500 65 2200
77
Table – 25: Statement showing the P/M3 cost of various forest produce as
mentioned under from the year 1996-97 to 2000-2001 in Hamirpur forest working
division.
Year Timber
P/M3
Fuel wood
P/M3
Charcoal
P/Qtls
Khair wood
P/M3
BL Logs
P/M3
Bamboo
P/Bundle
Resin
P/Qtl
1996-1997 2929 96 114 9577 0 0 0
1997-1998 3334 106 119 9577 0 0 0
1998-1999 3590 106 119 13313 4470 0 0
1999-2000 4812 106 119 15256 3721 0 0
2000-2001 4852 106 119 11564 2870 2494 2300
2001-2002 3800 182 400 11640 3050 0 2400
2002-2003 3230 182 400 11700 3100 27 2200
2003-2004 2670 185 400 11800 3250 0 2200
2004-2005 3200 220 485 19000 3500 0 2200
2005-2006 4000 231 485 18531 3800 0 2700
2006-2007 3400 300 509 20000 4000 0 2700
2007-2008 3400 360 728 23000 4000 0 2750
2008-2009 5000 360 738 30110 6000 0 3100
2009-2010 5000 360 738 22220 6500 0
2005-06 3200 400 500 18000 4000 0 2700
2006-07 4000 450 650 21500 3000 75 2700
2007-08 3400 500 750 24000 4000 0 2750
2008-09 5000 975 1100 30000 4700 0 3100
2009-10 5000 700 1000 25000 4000 0 3300
78
CHAPTER - IV
ACTIVITIES OF THE HP STATE FOREST DEVELOPMENT CORPORATION
4.1: HARVESTING AND MARKETING OF FOREST PRODUCE:
4.1.1: An undertaking of HP Govt:
H.P. State Forest Corporation Limited an undertaking of the HP Govt. came into existence on the 25th
of
March 1974. The Corporation deals with the marketing of mainly Timber, fuelwood, pulpwood,
bamboos, Khair, rosin, turpentine oil, subsidiary products (viz., phenyl, varnish, black Japan). In addition,
a timber seasoning & joinery unit at Baijnath is presently engaged in joinery works, timber chemical
treatment and timber seasoning for Government as well as private timber.
4.1.2: The objectives of Corporation:
The Corporation has been mainly created with the following objectives:
1. To carry out the extraction of timber and resin on scientific lines by adopting suitable modern
techniques.
2. To eliminate the Contractor's agency in respect of works of timber extraction and resin tapping.
3. To obviate the chances of illicit felling of trees, illicit tapping of resin and other malpractices.
4. To work the forests on commercial lines by recycling of funds for works and also by raising funds
from financial institutions as per requirements.
4.1.3: Expertise of Corporation:
The Corporation has got Expertise in the following:
4.1.4: RESIN PROCESSING:
With the two rosin factories working for more than three decades, the Corporation has fully trained staff
for this work and expertise in this respect is available for the purpose of resin processing into various
products and in their marketing. Notification of Himachal Pradesh Resin and Resin Products (Regulation
of Trade)Act,1981 is at appendix XVIII(A)
4.1.5: Awarding Tenders:
The schedule for inviting sealed tenders from registered Labour Supply Mates of appropriate category
for resin extraction and its carriage up to Road Side Depots ; felling, conversion and carriage of timber,
fuel wood, pulpwood, khair billets and bamboo bundles of various lots of fwds up to road side depots;
roping down of timber, truck transportation of timber and fuel wood of different lots of the various
Forest Working Divisions is fixed well in advance and these are received and opened on the same day at
the respective Divisional Offices (Hamirpur & Fatehpur) in the presence of tender(s) who wish to be
present at the time of opening of tenders. Negotiation of rates follow with the lowest tender(s).The
tenders are invited on prescribed form which can be obtained from the concerned office of the D.M.s @
Rs.100/- per form and are required to be submitted and accompanied with required EMD in shape of
FDR on Nationalized Bank duly pledged in favour of concerned Divisional Managers.
4.1.6: Jurisdiction of Forest Working Divisions:
Area of Nagrota Surian, Dada Siba and Dehra ranges falls under the jurisdiction of Forest Working
Division Fatehpur whereas Jwalamukhi range falls under the jurisdiction of Hamirpur FWD. The following
table will reveal the position in respect with the various product extractions from the Forests by these
Forest Working Divisions:
79
Table – 26: Statement showing details of Chil Govt. lots worked in Dehra FD through FWD, Fatehpur;
2001 to 2010
Year No.
lots
St. vol
marked
Target fixed Target achieved Dispatched
Timber Pulp F/w Timber Pulp F/w
2001 25 2957.87 887.00 60 0 696.658 40.00 00 696.658
2002 20 3938.45 733.00 0 200 695.140 0 180.00 695.140
2003 21 3529.98 987.00 70 0 910.614 54.00 0 910.614
2004 18 2495.49 624.100 100 0 580.132 97.50 0 580.12
2005 19 1872.18 472.500 50 0 418.134 40.00 0 418.134
2006 11 2472.64 703.00 85 0 678.883 75.00 0 678.883
2007 16 2023.70 630.00 20 0 550.358 15.00 0 550.358
2008 15 1965.98 590.00 35 0 560.190 25.00 0 560.190
2009 14 2017.57 605.00 15 0 410.123 10.00 0 388.416
2010 16 1833.81 550.00 25 0 35.321 20.00 0 26.635
Table – 27: Details of Chil Private lots worked in Dehra FD through FWD, Fatehpur; 2001 to 2010
Year No
Lots
St vol/
marked
Target fixed Target achieved Dispatched
Timber P/w F/w Timber P/w F/w
2001 0 0 0 0 0 0 0 0
2002 0 0 0 0 0 0 0 0
2003 0 0 0 0 0 0 0 0
2004 0 0 0 0 0 0 0 0
2005 0 0 0 0 0 0 0 0
2006 3 590.27 219.00 75 35 192.994 132.50 40.0 192.994
2007 0 0 0 0 0 0 0 0
2008 0 0 0 0 0 0 0 0
2009 14 3307.06 1245.84 335 0 804.550 362.00 0 804.550
2010 2 494.58 148.35 50 0 55.563 0 0 46.073
Table – 28: Lots worked in Dehra FD under FCA 1980, through FWD, Fatehpur; 2001 to 2010
Year No
lots
Area
Marked
Target M3 Target
Achieved
Dispatched
sold
2001 2 61.11 hac 56562 56562 56562
2002 1 25.01 hac 20000 21454 21454
2003 1 21.37 hac 15000 16914 16914
2004 1 27.72 hac 8000 14178 14178
2005 0 0 0 0 0
2006 1 98.66 hac 24500 24500 24500
2007 0 0 0 0 0
2008 0 0 0 0 0
2009 0 0 0 0 0
2010 1 61.11 hac 31000 13950 13950
80
Table – 29: Resin extracted from Dehra FD & dispatched to R & T Bilaspur; 2001 to 2010
Year Total
Blaze Total
Target Target
Achieved Sent to R
& T B/P Pure
Resin Remarks
2001 10162 392.52 396.27 396.27 388.36 --
2002 26834 992.13 856.63 856.63 844.38 --
2003 26206 995.15 896.24 896.24 884.77 --
2004 25408 1067.13 1069.47 1069.47 1048.22 --
2005 24680 1021.87 1029.86 1029.86 1010.96 --
2006 35019 1470.80 1444.66 1444.66 1433.20 --
2007 34160 1434.73 1430.89 1430.89 1383.34 14.45 Qtl Resin
Theft &
Recovery
received
2008 33630 1412.46 1361.36 1361.36 1334.43 --
2009 32529 1338.41 1245.59 1245.59 1201.96 --
2010 33594 1349.36 1242.53 1242.53 1209.01 --
282222 11474.56 10973.50 10973.50 10738.63 --
Table – 30: Details of Govt lots worked in Dehra FD through FWD, Hamirpur; 2001 to 2010
Year
No
of
lots
Achieved Dispatched
St Vol
C/coal
(Qtls) Timber P/w F/ w C/coal
2001-02 9 2770.62 0.000 547.126 67.000 916.000 0.00 547.126
2002-03 13 2742.99 425.000 1334.011 119.000 41.000 688.25 1334.011
2003-04 10 2478.97 568.000 936.646 79.500 41.000 775.00 936.646
2004-05 15 4064.08 582.000 1240.845 102.000 3.000 601.50 1240.845
2005-06 9 2456.17 387.000 646.636 31.000 6.000 515.60 646.636
2006-07 13 2205.6 421.000 678.452 43.000 190.000 202.25 678.452
2007-08 13 2060.22 302.500 710.607 30.000 186.000 250.00 710.607
2008-09 10 4417.2 460.000 1702.491 76.000 639.000 489.25 1702.491
2009-10 13 2943.85 357.000 431.080 12.000 104.000 110.00 431.080
2010-11 13 2524.57 0.000 0 0.000 0.000 0.000
81
Table – 31: Details of Pvt. lots worked in Dehra FD through FWD, Hamirpur: 2001 to 2010
Year
No
lots Target Achieved
2001-02 St Vol
Timber
m3
P/ w
m3
C/coal
(Qtls) Timber P/w F/w C/coal
2001-02 0 0 0 0 0 0 0 0 0.00
2002-03 0 0 0 0 0 0 0 0 0.00
2003-04 0 0 0 0 0 0 0 0 0.00
2004-05 0 0 0 0 0 0 0 0 0.00
2005-06 3 1023.57 411.0 11.000 75.000 417.000 40 20 50.00
2006-07 0 0 0 0 0 0 0 0 0.00
2007-08 0 0 0 0 0 0 0 0 0.00
2008-09 0 0 0 0 0 0 0 0 0.00
2009-10 1 95.30 28.000 10 0 0 0 0 0.00
2010-11 2 732.27 307.000 245.000 0 0 0 0
Table – 32: Govt. Chil Lots worked in Dehra FD through FWD Fatehpur, 2001 to 2010:
Year No
lots
St. vol
marked
Target fixed Target achieved Dispatched
Timber P/w F/w Timber P/w F/w
2001 25 2957.87 887.00 60 0 696.658 40.00 00 696.658
2002 20 3938.45 733.00 0 200 695.140 0 180 695.140
2003 21 3529.98 987.00 70 0 910.614 54.00 0 910.614
2004 18 2495.49 624.10 100 0 580.132 97.50 0 580.12
2005 19 1872.18 472.50 50 0 418.134 40.00 0 418.134
2006 11 2472.64 703.00 85 0 678.883 75.00 0 678.883
2007 16 2023.70 630.00 20 0 550.358 15.00 0 550.358
2008 15 1965.98 590.00 35 0 560.190 25.00 0 560.190
2009 14 2017.57 605.00 15 0 410.123 10.00 0 388.416
2010 16 1833.81 550.00 25 0 35.321 20.00 0 26.635
Table – 33: Pvt Chil lots worked in Dehra FD through FWD Fatehpur, 2001 to 2010:
Year No
lots
St.vol/
marked
Target fixed Target achieved Dispatched
Timber P/w F/w Timber P/w F/w
2001 0 0 0 0 0 0 0 0
2002 0 0 0 0 0 0 0 0
2003 0 0 0 0 0 0 0 0
2004 0 0 0 0 0 0 0 0
2005 0 0 0 0 0 0 0 0
2006 3 590.27 219.00 75 35 192.994 132.50 40.0 192.994
2007 0 0 0 0 0 0 0 0
2008 0 0 0 0 0 0 0 0
82
2009 14 3307.06 1245.84 335 0 804.550 362.00 0 804.550
2010 2 494.58 148.35 50 0 55.563 0 0 46.073
Table – 34: Details FCA removals in Dehra FD through FWD Fatehpur, 2001 to 2010:
Year No
lots
Stvol
mark
ed
Target fixed
Target achived
Dispatched
Timber P/w F/w Timber P/w F/w
2001 0 0 0 0 0 0 0
2002 0 0 0 0 0 0 0 0
2003 0 0 0 0 0 0 0 0
2004 0 0 0 0 0 0 0 0
2005 0 0 0 0 0 0 0 0
2006 0 0 0 0 0 0 0 0
2007 0 0 0 0 0 0 0 0
2008 0 0 0 0 0 0 0 0
2009 0 0 0 0 0 0 0 0
2010 1 42.6 9.799 3.00 0 9.810 14.00 0 9.810
Table – 35: Bomboo lots worked in Dehra FD through FWD Fatehpur, 2001 to 2010:
S
No
Year No
lots
Area
Marked
Target
fixed
Target
Achieved
Dispatched
1. 2001 2 61.11 hac 56562 56562 56562
2. 2002 1 25.01 hac 20000 21454 21454
3. 2003 1 21.37 hac 15000 16914 16914
4. 2004 1 27.72 hac 8000 14178 14178
5. 2005 0 0 0 0 0
6. 2006 1 98.66 hac 24500 24500 24500
7. 2007 0 0 0 0 0
8. 2008 0 0 0 0 0
9. 2009 0 0 0 0 0
10 2010 1 61.11 hac 31000 13950 13950
4.2.1:
The labour supply mates (LSMs) execute an agreement with the HPSFDC and make use of local labour
and also import labour from J&K and engage Nepali labour for carrying out many of the logging
operations. Extension of any kind in the working of lots hampers the plantation programme and
effective closure. Under the Himachal Pradesh Forests (protection from fire) Rules, 1999, the
corporation is duty bound to deploy sufficient staff to prevent and extinguish forest fires and checking of
illicit felling in consultation with the DFO as and when required.
83
4.3: Resin Tapping: Resin is obtained from Pinus roxburghi (chil) trees. Resin tapping started in 1912 in this region. The resin
tapping season starts from 15th
of March and lasts till 15th
November. The minimum diameter for
tapping chil trees is fixed at 35 cm dbh because trees at this diameter are suitable for obtaining
optimum yield.
4.3.1: RILL METHOD:
Loose bark over a surface area of about 45 X 30 cm is removed with the help of bark shaver leaving a
space of about 15 cm from the ground level. The bark left should not exceed 2 mm in thickness to
facilitate freshening. A Blaze frame is put in vertical position on the debarked area and outer
boundaries of the blaze are marked with black Japan. Position of the blaze and the central groove are
marked with the help of wooden board and marking gauge. A central groove is cut by drawing the
groove cutter from above downwards. Since in the first year the blaze is very near the ground, the
groove cutter is moved upwards. Central groove should be centrally placed. The lip is fixed with the
help of two horse shoe nails so that it makes an angle of 45o with the tree. A 5 cm long wire nail is
driven into the tree about 2 cm below the midpoint of the lip for hanging the collection pot on it. The
nail is driven at an angle so that the pot hangs snugly against the tree. It is suggested that instead of
wire nails, bamboo/wooden nails should be used for hanging the pot with tree. In the event of a fire
breaking out in the forest these wooden nails will get burnt and the pot will be dislodged from the
tree. The iron nail holds the pot fast to the tree and the burning resin in the pot acts like a blow lamp.
4.3.2: FRESHENING: First rill should be drawn by moving the freshening knife from the lowest point of
the central groove upwards along the blaze boundary in a way that rill makes an angle of 40* with the
central groove. The process is repeated on the other side of the central groove. For the second and
subsequent freshening which are repeated app. at weekly intervals, the guide of the freshening knife
should move touching the upper side of the previous rill. The rills should be parallel to each other with
an uncut bark (inter rill bark) of 5 mm in between two successive rills. Width of the rill is 6-7 mm and
depth 2 mm (excluding 2mm. Depth of unshaved bark). The length of rills should neither exceed nor fall
short of the blaze limit. One freshening is given almost every week and the blaze thus attains a height
(length) of 36-38 cm in one season. The tapping season is from 15th
March to 15th
November i.e. 8
months. Freshening is given 4 times in a month and thus the total no. of rills is to be limited to 32 in a
season. The width of the blaze is 20 cm i.e. 10 cm on either side of the central groove.
4.3.3: APPLICATION OF STIMULANT: The stimulant is a 20 percent solution of a mixture of sulphuric
and nitric acids mixed in equal proportion v/v. It should be sprayed on the freshly cut rill by squeezing
the plastic bottle and moving its nozzle in a steady motion along the rill. Precaution should be taken to
remove the pot till the extra acid has run down the lip. The tendency to apply stimulant more
frequently and in higher concentration to obtain higher yield should be curbed since it affects the tree
adversely.
4.3.4: TAPPING SEASON: Tapping season extends from 15
th March to 15
th November. Freshening are
not made from 16th
November to 30 November and during this period resin is scrapped (Raghod).
4.3.5: USE OF GUIDE: The use of guide with the rill knife by the tapper is compulsory.
84
4.3.6: INSTALLATION DURING SUBSEQUENT YEARS: For installation during the second year of tapping
the position of the blaze is marked above the top of first year blaze and other operations of first year are
repeated. After tapping for two years the blaze reaches a height at which it is not possible to pull the
freshening knife upwards. Hence during third year freshening is given by pushing the freshening knife
upwards (for the central groove towards the outer edge of the blaze). Like this the blasé is extended
upwards for four years. During fifth year it may be necessary to use a ladder. During 6th
year or in some
cases during 5th
year a new blaze is made at the bottom leaving 7.5 cm wide space from the outer edge
of the first year blasé.
85
CHAPTER-V
FORESTRY UNDER VARIOUS FIVE YEAR PLANS 5.1. GENERAL: In the past the forests of the division have been managed for getting
sustainable yield through various Working Plans. The silvicultural fellings were mainly aimed at
making the forest uniform and the regeneration achieved through natural means. The increasing
demands of forest produce in the state especially that of timber and fuel-wood resulted in focus
on large scale plantations of commercially important species. Although the plantation
programme started from Ist Five Year Plan but it gained momentum from IIIrd Plan
onwards.The Plan wise management of forests and expenditure is as under:
5.2. Ist FIVE YEAR PLAN (1951-56):- During Ist Five Year Plan the forests of this
division were managed under Romesh’s revised working plan (1950-51 to 1980). The forests of
the tract were exploited commercially to meet the timber and fuel-wood requiremets. Chil
Shelterwood, , Coppice and Selection working circles were constituted and worked. The
Protection and Plantation were created to improve the condition of the growing stock and meet
local demand of fuel and fodder. The Chil Shelterwood under “Punjab Shelterwood System”
with mainly artificial regeneration. However, in Coppice working circle the silvicultral system
adopted was “Coppice with Standard” whereas in Plantation working circle “Clear Felling
System” followed by plantation of chil was preferred. The combined figures of revenue and
expenditure during Ist Five Plan of Dehra Forest Division are tabulated as under
Table: 36: Revenue and Expenditure during Ist Five Year Plan
Year Revenue in Rs. Expenditure in Rs. Surplus/Deficit
in Rs. (+)/(-)
1951-52 NA NA NA
1952-53 NA NA NA
1953-54 NA NA NA
1954-55 NA NA NA
1955-56 NA NA NA
Source: Dehra Forest Division.
5.3. IInd FIVE YEAR PLAN (1956-61):- ):- During I1 Five Year Plan the forests of this
division were managed under Romesh’s revised working plan (1950-51 to 1980). The forests of
the tract were exploited commercially to meet the timber and fuel-wood requiremets as above.
52
Table: 37. Revenue and Expenditure during IInd Five Year Plan
Year Revenue in Rs. Expenditure in Rs. Surplus/Deficit
in Rs. (+)/(-)
1956-57 NA NA NA
1957-58 NA NA NA
1958-59 NA NA NA
1959-60 NA NA NA
1960-61 NA NA NA
Source: Dehra Forest Division.
86
5.4. IIIrd FIVE YEAR PLAN (1961-66):- During this period, the forests of this tract
were managed under under Romesh’s revised working plan (1950-51 to 1981-82) as above. The
combined figures of revenue and expenditure during IIIrd Five Plan of Dehra Forest Division are
tabulated as under in Table:
Table: 38- Revenue and Expenditure during IIIrd Five Year Plan
Year Revenue in Rs. Expenditure in Rs. Surplus/Deficit
in Rs. (+)/(-)
1961-62 NA NA NA
1962-63 NA NA NA
1963-64 NA NA NA
1964-65 NA NA NA
1965-66 NA NA NA
Source: Dehra Forest Division.
5.5. IVth FIVE YEAR PLAN (1969-74):- During this period, the Forests this division were
managed under MALHOTRA’S REVISED WORKING PLAN (1966-67 TO 1980-81): Even
though Romesh Plan was to expire in 1980-81 with the provision for interim revision after I5
years the reorganization of the Division coupled with the desirability of bringing vast Un-
delimited Protected and Un-classed Forests under regular management necessitated complete
revision of the plan from 1966-67 itself. The revised plan included all the Delimited Protected,
Un-delimited Protected and Un-classed Forests of the Divisions, except those under Cooperative
Forest Societies. The following WCs were constituted:1.The Chil Shelter wood Working Circle.
2.The Oak Shelter wood Working Circle. 3.The Coppice Working Circle. 4.The Khair
(Overlapping) Working Circle. 5.The Plantation Working Circle. 6.The Avenue Working Circle.
7.TheProtectionWorkingCircle.8.TheGrazing(overlapping) Working Circle. The combined
figures of revenue and expenditure during IInd Five Plan of Dehra Forest Division.
Table: 39-Revenue and Expenditure during IVth Five Year Plan
Year Revenue in Rs. Expenditure in Rs. Surplus/Deficit
in Rs. (+)/(-)
1969-70 3755290* 3189314* (+)565976
1970-71 3669460* 4206414* [-] 536954
1971-72 7862581* 5856818* [+] 2005763
1972-73 3300439* 6832815* (-)3532376
1973-74 9229613* 6506197* (+)2723416
5.6. Vth FIVE YEAR PLAN (1974-79):- During this period, ):- During this period, the Forests
this division were managed under MALHOTRA’S REVISED WORKING PLAN (1966-67 TO
1980-81):
The figures of revenue and expenditure during Vth Five Plan of Dehra Forest Division are
tabulated as under in Table:
Table: 40(A)- Revenue and Expenditure during Vth Five Year Plan
Source:
Baldev
Singh `s
W.P. of
Una
F.D.&
Year Revenue in Rs. Expenditure in Rs. Surplus/Deficit
in Rs. (+)/(-)
1974-75 6282050* 7687996* (-)1405946
1975-76 8741329* 5532270* [+] 3209059
1976-77 3085870* 1862071* [+] 1223799
1977-78 7610122* 2167884* (+)5442238
1978-79 8106395* 6934936* (+)1141459
87
M.P. Singh`s W.P. of Dharamsala F.D.
5.7. VIth FIVE YEAR PLAN (1980-85) : The forests of this tract were managed under
M.P.SINGH Working PLAN, (1981-82 TO 1995-96) as applicable to Right bank of the river
Beas which comprises the present Jawalamukhi, Nagrota Surian and two blocks of Dehra range
(Dehra and Bankhandi) and were worked under following Working Circles:The Chil Shelter
Wood Working Circle; The Coppice Working Circle; The Plantation Working Circle; The
Protection Working Circle; The Khair (Over lapping) Working Circle & The Wild Life (Over
lapping) Working Circle and : Baldev Singh 5th
WP for the Forest of Una and Dehra (Part)
Divisions 1981-82 to 1995-96 (Left Bank of River Beas) comprising of Protection Working
Circle, Khair (Over lapping) Working Circle ,the Chil Shelter Wood Working Circle .
The figures of revenue and expenditure during VIth Five Plan of Dehra Forest Division are
tabulated as under in Table:
Table: 40(B) Revenue and Expenditure during VIth Five Year Plan
Source:
Baldev
Singh `s
W.P. of
Una
F.D.&
M.P.
Singh`s
W.P. of Dharamsala F.D.
5.8. VIIth FIVE YEAR PLAN (1985-90): - During this period, the forests of this tract were
managed under under managed under M.P.SINGH Working PLAN, (1981-82 TO 1995-96) and
54
Baldev Singh 5th
WP for the Forest of Una and Dehra (Part) Divisions 1981-82 to 1995-96 as
above. The social forestry works were in full swing, main emphasis being on raising fuel, fodder,
small timber and grasses to meet the increasing domestic needs of rural communities. The
figures of revenue and expenditure during VIIth Five Plan of Dehra Forest Division are tabulated
as under in Table:
Table:40(C)- Revenue and Expenditure during VIIth Five Year Plan
Source:
HP
FORES
T
STATI
STICS
1990
5.9. VIII FIVE YEAR PLAN (1992-97): -) During this period, the forests of this tract were
managed under under managed under M.P.SINGH Working PLAN, (1981-82 TO 1995-96) and
Baldev Singh 5th
WP for the Forest of Una and Dehra (Part) Divisions 1981-82 to 1995-96 as
above . The JFM approach also started in the division and the forestry activities were
implemented under departmental schemes. Due to ban on green felling, the objective was
Year Revenue in Rs. Expenditure in Rs. Surplus/Deficit in
Rs. (+)/(-)
1980-81 11303953* 4272242* (+)
1981-82 4642692* 3338619* (+)
1982-83 NA NA NA
1983-84 NA NA NA
1984-85 NA NA NA
Year Revenue in Rs. Expenditure in
Rs.
Surplus/Deficit in
Rs. (+)/(-)
1985-86 NA NA NA
1986-87 610000 8512000 (-)7902000
1987-88 668000 11333000 (-)10665000
1988-89 356000 10750000 (-)10394000
1989-90 NA NA NA
88
afforesting denuded/degraded forests. The constitution of forest development committees and
their participation in planning and implementation was sought. The figures of revenue and
expenditure during VIIIth Five Plan of Dehra Forest Division are tabulated as under.Table:.
40(D) Revenue and Expenditure during VIIIth Five Year Plan
Source:
Dehra
Forest
Divisio
n.
5.10.
IXth
FIVE YEAR PLAN (1997-2002):- The JFM activities continued in this perod and Due to ban on green
felling, the objective was mainly on afforesting denuded/degraded forests. The works of
afforestration, soil conservation, entry point activity started by the VFDCs and microplan process
learnt and executed. Sanjhi Van Yojna started on the principles of JFPM. Here again the focus
remained on restocking/regeneration of degraded forests. The figures of revenue and expenditure
during IXth Five Plan of Dehra Forest Division are tabulated as under.
55
Table: 40(E)- Revenue and Expenditure during IXth Five Year Plan
Source:
Dehra
Forest
Divisio
n.
5.11.
Xth FIVE YEAR PLAN (2002-2007): - Both the JFM programmes & SVY created mass awareness
about forestry but the focus was again on raising plantations besides soil works and entry point
activities other Compensatory Afforestation was also implemented with emphasis on soil, water
conservation. Due to ban on green felling only salvage removals has been carried out with focus
on planting open and denuded forests. The figures of revenue and expenditure during Xth Five
Plan of Dehra Forest Division are tabulated as under.
Table: 40(F) -Revenue and Expenditure during Xth Five Year Plan
Source:
Dehra
Forest
Divisio
n.
5.12.
XIth FIVE YEAR PLAN (2007-2012): - Both the JFM programmes & SVY created mass awareness
about forestry but the focus again is on raising plantations/increasing forest cover besides soil
Year Revenue in Rs. Expenditure in
Rs.
Surplus/Deficit in
Rs. (+)/(-)
1992-93 18,000 2,80,74,075 [-] 2,80,56,075
1993-94 1,65,107 6,22,00,892 [-] 6,20,35,785
1994-95 4,29,000 57,28,581 [-] 52,99,581
1995-96 5,41,898 59,92,773 [-] 54,50,875
1996-97 6,18,000 59,97,739 [-] 53,79,739
Year Revenue in Rs. Expenditure in
Rs.
Surplus/Deficit in
Rs. (+)/(-)
1997-98 4,99,000 52,44,900 (-) 47,45,900/-
1998-99 5,50,000 68,88,802 (-) 63,38,802/-
1999-2000 18,15,447 95,70,326 (-) 77,54,879/-
2000-01 14,56,000 90,60,252 (-) 76,04,253/-
2001-02 11,13,000 95,17,177 (-) 84,04,177/-
Year Revenue in Rs. Expenditure in
Rs.
Surplus/Deficit in
Rs. (+)/(-)
2002-03 31,38,964 79,04,689 (-) 47,65,725/-
2003-04 10,12,792 49,02,032 (-) 38,89,240/-
2004-05 9,72,419 49,54,650 (-) 39,82,231/-
2005-06 53,17,314 1,29,57,138 (-)76,39,824 /-
2006-07 29,18,306 1,20,04,300 (-) 90,85,994/-
89
works and other Compensatory Afforestation are being implemented with emphasis on soil,
water conservation. Due to ban on green felling only salvage removals has been carried out with
focus on planting open and denuded forests. The figures of revenue and expenditure during XIth
Five Plan upto 2010-11of Dehra Forest Division are tabulated as under.
Table: 40(G)- Revenue and Expenditure during XIth Five Year Plan
Source:
Dehra
Forest
Divisio
n
*These are combined figures as present Dehra Forest Division was managed under Dharamsala
and Una Forest Division prior to 1984.
P.56
Year Revenue in Rs. Expenditure in
Rs.
Surplus/Deficit in
Rs. (+)/(-)
2007-08 13,03,448/- 74,36,959/- (-) 61,33,511/-
2008-09 11,71,288/- 66,37,950/- (-) 54,66,662 /-
2009-10 15,34,339/- 75,65,850/- (-) 60,31,511/-
90
C H A P T E R - V I
S T A F F A N D L A B O U R S U P P L Y
6 . 1 : S T A F F :
T a b l e 4 1 : Position of Staff as on 01 Jan 2012:
Category Sanctioned Existing Shortfall
Plan Non Plan Plan Non Plan Plan Non Plan
DCF 1 1 0
ACF 2 2 0
FRO 6 1 -5
DR 19 18 -1
FGd 75 61 -14
SUPDT 1 1 0
Sr ASST 3 3 0
CLERK 6 3 -3
KANUNGO 1 1 0
DRIVER 1 1 0
PEON 8 13 5
F.WORKER 30 30 0
MALI 4 4 0
CHOWKIDAR 6 6 0
PEON CUM-
CHOWKIDAR 2 0 -2
TIMBER
WATCHER 1 1 0
PATWARI 1 0 -1
SWEEPER 1 0 -1
PEON CUM
KHALASI 2 0 -2
6 . 2 : In 1978, Dharamsala and Palampur forest divisions were carved out of the erstwhile Kangra Forest
Division. Again in June 1984, when Dehra forest division was constituted, part of Jwalamukhi and
Nagrota Surian ranges of Dharamshala FD and Dada Siba range of Una forest division were merged to
form the new Dehra FD. The present WP thus covers 4 ranges viz Jawalamukhi, Nagrota Surian, Dehra
and Dada Siba. The Pong reservoir is separate and under the Wildlife Wing with two ranges at Nagrota
Surian and Dhameta.
6.3: There appears to be a chronic problem with both clerical and field staff deployment. Clerical staff
has not been recruited for over two decades now, with the result that while there are adequate number
of senior assistants, there is a shortage of clerks. This directly affects office working as more often than
not, senior assistants are unwilling to do the work of clerks. Also, over the years there has been an
exponential increase in paper work at the DFO level. While adequate numbers of computers are now
available in the DFO’s office, these are mainly used as expensive typewriters. The clerical staff is not
adequately trained to make fuller use of computers. With a few exceptions e-mail is generally not used
91
for even routine correspondence and hundreds of letters are printed and signed as was done in earlier
times. There is thus a dire need to increasingly use the electronic format for correspondence and for
regular accounts and tabulation work which is substantial. Many Range offices also have computers, but
few have staff / forest guards who can properly operate these.
6.4: At the field level due to irregular and mass recruitments after gaps of decades, the age structure of
forest guards and block officers and range officers has got skewed. The average age of most of these
field staff is well over 50 years.
6.5: There is now a huge network of roads in most divisions. However, in the forest department a typical
forest division has only one vehicle, exclusively for the DFO’s use. This places severe restriction on staff
mobility and consequently on proper discharge of their duties. One vehicle at the Range level is now
absolutely necessary and in lower divisions like Dehra, forest guards and forest workers in many beats
can at least be provided with bicycles.
6.2: LABOUR SUPPLY:
Forest exploitation is being done through HPSFC. They get labour from Nepal and J&K. Locally charcoal &
fuel wood is generally extracted by the inhabitants of the area from their private land through the local
labour. For the other Forestry operations like planting, raising nurseries, seed collection, building, road
and path constructions etc. local labour is utilized by the forest department.
Table 42: Daily wage rates changes since 1987 (Rs/day)
Month/year Unskilled labour Driver Clerk
11/1987 16 - -
05/1989 18 - -
06/1989 19 - -
01/1990 20 - -
01/1991 22 - -
12/1993 24 - -
10/1994 26 28 -
04/1995 45.75 62.50 57.95
03/1996 45.75 63.47 63.47
08/1998 51 69.50 65
08/2001 55 75 70.50
08/2002 60 81 76
08/2003 65 88 82.50
08/2005 70 95 89
01/2007 75 102 95.50
01/2008 100 136 127
03/2009 110 150 140
10/2010 120 164 153
92
CHAPTER VII
PAST SYSTEMS OF MANAGEMENT
7.1: Early History of Guler State:
“In its palmy days Guler State extended from Ganesh- Ghati in the east to Reh in the west, and
from the Bias in the south to Gangot and Jawali in the north. It has the same limits as the present
Dehra tahsil, if Datarpur be added and tappa Gangot excluded. The peculiar circumstances in
which it was founded have already been related in the history of Kangra State, and local tradition
fully confirms the details of the story. The well into which Hari- Chand fell is still shown.
The original name if the State was Gwaliar of which Guler is a derivation, and it is several times
referred to under this name in the Mohammedan histories. The name is derived from the word
Gopala or Gwala, meaning “a cowherd.” And the tradition is that a cowherd pointed out to Hari-
Chand the site, where a tiger and a goat were seen drinking water together, as a suitable place for
his capital. In keeping with the custom of the time, the cowherd was offered as a sacrifice, and
his head buried in the foundation to ensure the stability of the fort.
In addition to the Guler Fort at the capital, called Haripur Fort, there were six other forts along
the frontiers of the State. These were Mastgarh, Kotla, Nahklanok, Gandharp, Ramgarh and
Mangarh. Of these Kotla was the most important.
Gwaliar is referred to under that name in the Tarikh-i-Mubarak Shahi, Tabaqat-i-Akbari, Tarikh-
i-Daudi, and the Akbarnamah; there is also a chronicle of Guler State, called Diliparanjani,
which was written during the reign of Dalip Singh, in Vik. 1762 (A.D. 1705). It is in old Hindi
verse, and is the chief authority for the history of the State.
Raja Hari-Chand is said to have settled first at Harsar where he fell into the well, but soon
afterwards moved to Guler or the place now bearing that name. He then founded the Fort of
Haripur at the end of a ridge overhanging the Banganga river, one of the most striking and
picturesque situations in the Kangra District. It was originally a fortified palace rather than a
fortress, which the Sikhs at a later time fortified. The two outer gateways were demolished in
1847, and much destruction was caused by the earthquake of 1905, and it is now in a ruinous
condition.
Hari-Chand also founded the town of Haripur on the flat below the fort, near the left bank of the
Banganaga, and an older town, called Purana Guler, stands on the right bank, where Hari-Chand
perhaps resided while the fort was being built. Very little information is available about the early
history of the State, after Hari-Chand.
Ram- Chand, c. A.D. 1540- Ram-Chand was the fifteenth Raja in direct succession after Hari-
Chand, covering a period of about a hundred and twenty years, and giving a reign of only eight
years to each. This is much below the general average in the Hill States. During this period there
is only one reference to the State in contemporaneous history. This is in the Tarikh-i-Mubarak
Shahi where we read that Prince Nasir-ud-Din Muhammad Tughlaq, eldest son of Firoz Shah
Tughlaq, being compelled, in A.D. 1388, to flee from Delhi, was pursued as far as Suket and
Gwaliar on his way to Nagarkot.
Jagdish-Chand, c. A.D. 1570 - The Raja of Guler referred to as Parsuram was doubtless the Ram-
Chand of the Vansavali, who is again mentioned at a later date, in connection with the expedition
dispatched by Akbar in A.D. 1572, to suppress a revolt in the hills.
Rup-Chand, c. A.D. 1610 - Rup-Chand was the most notable of the Guleria Chiefs. He must
have succeeded about A.D. 1610, and remained loyal throughout his reign. He took an active
93
part in the final siege of Kangra Fort in the reign of Jahangir, which surrendered to the Imperial
army on Thursday, 1st Muharram, A.H. 1029 (16
th November 1620 A.D.). In the Tuzuk-i-
Jahangiri the following occurs:
“As Raja Rup-Chand of Gwaliar had been very active in his service at Kangra, an order was
given to the Chief diwans to hand over half of his native place to him in free gift, and the
remaining half as a tankhwah (salary) jagir.” The date of this order was Thursday, 26th
Azar,
A.H. 1030, corresponding to 7th
December, 1621 A.D., and shortly afterwards he was honoured
with the gift of an elephant and a horse and was granted leave to go to his State.
Again in A.D.1623-24, Rup Chand of Gwaliar is mentioned among the Amirs who had been
appointed to suppress a disturbance raised by Raja Jagat Singh of Nurpur, at the instigation of
Prince Khurram (Shahjahan), who was then on bad terms with his father.
In the Guler chronicle, already referred to, the bard states that Rup Chand overran the hill
districts twenty-two, that is many times, in the service of the Emperor Jahangir, and received the
title of Bahadur and khilat and two weapons, still preserved in the family preserved in the family.
He was also sent on a military expedition to the Dakhan where he distinguished himself. On his
return he was honored with Khilats and permitted to retire to his State.
Finally in the same record an account is given of an expedition against Garhwal State, in which
Rup Chand bore an honorable part and lost his life.
Guler probably came under the control of Ghamand-Chand of Kangra from about 1758, and
under the Sikhs at a later date, till 1786, when Raja Sansar-Chand acquired supreme power in the
hills. But amid all these changes the Guler State continued to preserve its integrity, except the
ilaqa of Kotla, which originally belonged to the State.
Kotla ilaqa seems to have been a part of the Imperial demesne formed by Todar-Mal in the reign
of Akbar, and the fort was garrisoned with Mughal troops, probably from the same time as
Kangra Fort, It is not known when the garrison was evacuated, but in 1785 it was captured by
Dhian-Singh, Wazir of Guler, who made himself independent and successfully resisted even
Sansar-Chand, in the height of his power.
Bhup-Singh, c. A.D. 1790 - Bhup-Singh who came to the gaddi about 1790 was the last ruling
Chief of Guler. All the Kangra States were then under the supremacy of Sansar-Chand, and his
oppressive measures aroused a spirit of resistances among them. They formed a confederacy
against him, and through the Raja of Bilaspur invited the Gurkhas to invade Kangra. Bhup Singh
was one of the first to join them with his contingent.
On the expulsion of the Gurkhas and the surrender to Kangra Fort to Ranjit-Singh in 1809, all the
States of the Kangra group came under his control. For a time he treated Bhup-Singh with
respect and called him Baba, but the extinction of the principality was close at hand. In 1811
Ranjit-Singh began to disclose his designs on the Hill States, and Guler was the first to be
annexed. In that year Desa Singh Majithia was sent against Kotla Fort and captured it in a week,
a jagir being assigned to Wazir Dhian-Singh in the Doab. In 1813 the rest of Guler State was
also seized. Mr. Barnes gives the following account of the way in which this was done:-
“The plan was skillfully and deliberately laid. The Raja was directed to raise a large force to
assist in some operations on the Indus, and when the military strength of the population was
drained off and the country lay defenceless, the Raja was summoned to Lahore. On the day that
he expected leave to return, he was shamelessly arrested, and told that he would not be alloed to
go till he surrendered his kingdom and accepted a jagir. Without waiting for a reply, Desa-Singh
was sent off with an army of ten thousand Sikhs, and the territory was quietly annexed to the
growing rule of the Khalsa. The Raja was restored to liberty, but spurned the offer of a Jagir. He
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had, however, assigned 20,000 rupees during his own incumbency for the support of his female
household; and Ranjit-Singh left that maintenance untouched.” These lands still form the Jagir
of the family.
Bhup-Singh died in 1820 and was succeeded by his son, Shamsher-Singh.
In the first Sikh War he raised a force form among his retainers and turned the Sikhs out of
Haripur Fort. Shamsher Singh remained loyal during the rising of 1848 and refused to
countenance the proceedings of his kinsmen. He died in 1877”.
7.2: Siba State: “Siba State was an offshoot from Guler, as Guler was from Kangra, In the fourth generation after
Raja Hari-Chand, as younger brother of the ruling Chief of Guler, named Sibaran-Chand, ,made
himself independent in a tract to the south of the Bias, probably about A.D. 1450.
There he founded his capital and called it Siba after his own name, and in accordance with
ancient custom the name was also applied to the State. Taluqa Siba in the Kangra District at the
present time, represents the exact dimensions of the former State. The clan name is Sibaia.
There were 25 Rajas in succession after Sibarn-Chand :- Hami-Chand, Pahlad-Chand, Jit-
Chand, Udhan-Chand, Autar-Chand, Rup-Chand, Manak-Chand, Nirmodh-Chand, Jap-Chand,
Kilas-Chand, Prag-Chand, Sansar-Chand, Narain-Chand, Trilok-Chand, Kishan-Chand, Jai-
Chand, Prithi-Chand, Amar-Chand, Jaswant-Singh, Bhag-Singh, Lakel-Singh, Madho-Singh,
Sher-Singh, Gobind-Singh, Ram-Singh, giving an average reign of only nine years.
Very little is known of its subsequent history, but Siba is mentioned in Jahangir’s memoirs on
the occasion of his visit to Kangra in January A.D. 1622. He was accompanied by Nurjahan
Begam and her father, Itimad-ud-daula ; and when the Imperial camp was at the Village of
Bahlun in Siba the Emperor set out with his personal retinue to visit Kangra Fort, leaving
Nurjahan with her father who was seriously ill. On the way a messenger overtook him with a
Message that grave symptoms had appeared, and Jahangir atonce retraced his steps and was
present at Itimad-ud-daula’s death. He then went on to Kangra, probably by Haripur, and
returned by Nurpur. The State seems to have preserved its independence all through the Mughal
period under its own Rajas, of whom there were 26 down to the time of its extinction. It was
subject to the Sikhs like the other Hill States, and to Sansar-Chand of Kangra from 1786 till the
Gurkha invasion in 1806, and the Raja of that time was Gobind-Singh. Availing himself of the
disorder then prevailing, Raja Bhup-Singh of Guler, in 1808, invaded Siba and annexed it, It
came under Ranjit-Singh along with Guler and the other Hill States in 1809, and ten years later
he disjoined it from Guler, and in 1830 restored it to Raja Gobind – Singh. Amid the ruin that
befell the other Hill States in Kangra, Siba alone escaped. It is said that Ranjit-Singh had doomed
it to destruction, but it was saved owing to the fact the Raja Dhian- Singh, the Minster, had
obtained two princesses of the Siba family in marriage, and through his intervention the danger
was averted, A tribute of Rs. 1,500 was imposed, and the principal fort had to be surrendered, but
the State was left intact, as a jagir.
The Territory was then divided between the two cousins, Raja Gobind-Singh and Mian Devi-
Singh ; lands worth Rs. 20,000 (subject to tribute ) being assigned to the former and of Rs. 5,000
(taluqa Kotila ) to the latter.
Raja Gobind-Singh died in 1845 and was succeeded by his son, Raja Ram- Singh. During the
second Sikh War he drove the Sikhs out of Siba Fort, and also ousted his cousin, Bijai-Singh, son
of Devi- Singh, from his jagir, but was obliged to restore it. Raja Ram-Singh died without heirs
in 1874, and his jagir was re-granted to Bijai-Singh and his heirs-male in perpetuity, subject to
an annual tribute of Rs. 1,500. He was followed by Raja Jai-Singh, who died in 1920; and after
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him his son, Raja Gajinder-Singh, who died in 1926. Raja Sham-Singh is the present head of the
family. The State is generally spoken of as Dada-Siba from the two principal places within its
bounds.
On 15th
March, 1919 the title of “Raja” was officially conferred on Jai-Singh, Jagirdar of Siba,
as a hereditary distinction, by Government”.
[Excerpted from THE HISTORY OF THE PUNJAB HILL STATES, ]
]
7.3: Dehra Forests in the Past: “The dehra tahsil may be described in a general way as occupying both sides of the valley of the
Bias, from Nadaun in the Kangra district to near Talwara, where the Bias first touches the
Hoshiarpur district. North of the Bias the country is much broken up by irregular ranges of hills,
the most conspicuous of which is the Kalidhar ridge, which rises to 3,728 feet (1133m). The
general direction of these hills is, as in the rest to Kangra proper, from north-west to south-east.
To the south of the Bias river the valley is shut in by the Sole Singhi or Jaswan range, and its
numerous spurs which spread out and descend from the central ridge, which is between 3,000
and 4,000 feet high, to the Bias river, a distance of about ten miles. The Dehra tahsil includes the
jagirs of the Rajas of Goler and Siba on the right and left banks of the Bias river, about ten miles
below Dehra. The forests in the Dehra tahsil consist partly of chil (Pinus longifolia), and partly
of other trees, such as Kembal (Odina wodier) ; kalam (Stephegyne parvifolia) ; dhau
(Anogeissus latifolia) ; jaman (Eugenia jambolanum) ; amaltas or Indian Laburnum (Cassia
fistula) ; khair (Acacia catechu) ; bahera (Terminalia bellerica) ; kamal (Mallotus phillipinensis) ;
sirin (Albizzia julibrissin) ; kilawa (Wrightia tomentosa) ; keor (Holarrhena antidysenterica) ; bil
(Aegle marmelos); amla (Phyllanthus emblica) ; chilla (Casearia tomentosa) ; sanan (Ougeinia
dalbergiodes) ; kakran (Pistacia integerrina) ; karal (Bauhinia variegata ); kainth (Feronia
elephantum ) ; ambara (Spondias mangifera) ; and a variety of other trees and bushes. There is
also a sprinkling of bamboos (Dendrocalamus strictus) in one or two places; but the last
mentioned is at its extreme natural limit, and never attains any large size.
“In 1875 an agreement was made with certain village communities in the Dehra tahsil whereby
they gave Government 48 blocks of forest since declared reserves under Section 34 of the Forest
Act, and aggregating 11,067 acres (about 4429 ha) or about 17 square miles, in full proprietary
right. Government on their part surrendered the right to close any part of the remaining forest or
waste land within the village bounds, and agreed to give the village community a third share of
the forest revenue derived there form. The area of unassessed waste lands, including unreserved
forest areas and exclusive of roads, nallas, rivers and village sites, is estimated at about 110
square miles. Except where modified by the mutual agreement above mentioned, the rights of
Government and of the people in the Dehra forest are very much the same as in Hamirpur,
already described, the only difference being that in Dehra, where inferior species of trees
abound, chil is not granted, as in Hamirpur free of charge. Chil timber is the principal forest
product exported from the Dehra forests, and the mode of sale and extraction is similar to that
adopted in Hamirpur except that one or two of the more accessible forests have occasionally
been worked by departmental agency. The forests in the jagirs of Goler and Siba, which are
composed of chil, bamboos and miscellanies trees, are managed by the Rajas, subject to the
control of the Forest Department, Government being also entitled to a certain share in the forest
revenue”.
(EXTRACT from: THE KANGRA DISTRICT GAZETTEER, 1883).
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(Mainly excerpted from MP Singh’s WP, 1980-81 to 1995-96)
7.4: GENERAL HISTORY OF THE FORESTS:
Before the tract ceded to the British on 9th
March in 1846, the forests were the property of the
local ruler where definite rules for forest management existed. On the advent of British rule, the
forests were placed under the control of Deputy Commissioner, who managed them according to
the rules embodied in the village administration papers of the Land Revenue Settlement by
Barnes (1849-52). These Rules, a mere re-iteration of ancient practice, were modified by Bailey
in 1853 which in 1859 were replaced by local Rules applied under the authority of the “Rules for
the Conservancy of Forests in the Hill tracts of Punjab” promulgated by Govt. of India in 1855.
In 1870, as a preliminary to the constitution of reserved forests on the principles followed in
Hoshiarpur district, Dehra tehsil forests were placed under the control of the Forest Department.
Reserves in Dehra tehsil were notified in 1879 vide Notification No. 111-F dated 6th
March,
1879. 6 blocks of forests in Dada-siba jagir were demarcated during Barnes Settlement (1848) and the
draft notification was prepared. Simultaneously, the provisions of Chapter-IV of the IFA, 1878 to
all wastelands, demarcated and un-demarcated were also proposed to be applied. The
notification, however, could not be issued till Sheep Shank was deputed as Forest Settlement
Officer, who submitted his report in 1913 and Notification No 2839-A to 2839-E all of 31st
August 1915 were finally issued.
7.4.1: The year 1878 saw the introduction of Indian Forest Act for the first time where upon
regular Forest Settlement commenced in 1883. The forests of the tract were placed under the
control of Forest Department in 1894. After promulgation of Anderson’s Forest Settlement in
1897, the first Working Plan was compiled by Hart (1903-04 to 1921- 22).
7.4.2: In 1909 the Govt. of India drew attention of Punjab Govt. to the unsatisfactory condition
of most the Protected Forests, the ever increasing demand of right holders, the excessive sheep
and goat grazing etc and directed for taking remedial measures for preventing forests from
permanent damage. This resulted in the imposition of “Cattle Tax”, enhancement in gaddi
grazing fee, a scheme of Rotational Closure of the forests and creation of two forest authorities
in the district in the year 1920. The Delimited Protected Forest covered by the scheme of
Rotational Closure remained under the charge of Forest Department while the remaining forests
were again placed under the control of Deputy Commissioner, who employed separate staff for
their protection and management. A revised working plan for the management o forests under
the control of Forest Department was prepared by Walters (1920-21 to 1929-30). However, in
1924 the Punjab Legislative Council refused to provide funds to the establishment. As a result
the Forest Department resumed charge of these forests also.
7.4.3: The Dharamshala Municipa1 Forests were constituted in 1867, when forests of mauza
Kareri and Dharamshla were transferred to the charge of Dharamshala Municipality as grant-in-
aid; with the stipulation that no octroi will be imposed, with the objective of helping the poor.
Assisted by a few Rakhas, the Kotwal managed these forests up to 1894. As a sequel to the
condemnation of the arrangement in Anderson’s Settlement Report, the management of these
forests was transferred to work the forests most economically and pay the net revenue to the
Municipality. In 1902 Blaschek prepared a scheme of felling for 20 years, which was not acted
97
upon till 1913. These forests were first brought under regular management in the Walter’s
revised Working Plan from 1920 along with other forests.
7.4.4: For saving Dharamshala town from serious landslips and erosion, the area above the town
acquired in 1914 and declared as Reserved Forest. The first working scheme for the Reserved
Forest, (Reserved Banal) was prepared for five years from 1915 to 1920. The second working
scheme was prepared by Budhi Singh (1922 to 1933). A revised working scheme from 1933 to
1938 was prepared by David followed by the revised working scheme of Aggarwal (1942 to
1951). The last revised working scheme was prepared by Romesh (1952-53 to 1961-62) where
after the forests were incorporated in the main revised working plan of Kangra Forest Division
by Malhotra (1966-67 to 1980-81).
7.4.5: The working scheme for Kangra Municipal Forest, by Agya Ram (1960-61 to 1974-75)
was prepared in pursuance of Punjab Govt. letter No. 1427-.Ft-57/12O3 dated 20.5.1957,
transferring an area of 42.90 ha on certain conditions.
7.4.6: The Railway Strip’s Working Plan from 1953-54 to 1974-75 was prepared by Swam
Singh which dealt with the side strips of the 52 kilometer railway tract of Pathankot-
Jogindernagar section falling within the then Kangra Forest Division.
7.4.7: From 1931-32 to 1950-51 the forests were managed under Mohan’s Revised Working
Plan for Kangra Forest Division. This Working Plan dealt with only the Delimited Protected and
some more important Un-classed Forests. Mohan’s Plan was followed by Revised Working Plan
(1951-52 to 1980-81) prepared by Romesh which also dealt with only the Delimited Protected
and some Un-classed Forests of the main valley. Some forests of the main valley were
transferred to the Cooperative Forests Societies for management during 1941 and separate
Working Plans were compiled for each society followed by an Integrated Working Plan for the
district by Rawal (1968-69 to 1982-83). An intermediate revision of Romesh Plan was carried
out by Malhotra (1966-67 to 1980-81) which dealt with all the Delimited Protected, Un-
delimited Protected and Un-classed Forests of the Kangra Forest Division.
7.8: PAST SYSTEMS OF MANAGEMENT AND THEIR RESULTS:
The period between 1846 and 1980-81 can be divided into threé distinct periods from the
management stand point.
(i) The Period of Organization (1846-1894) : The forests remained under the charge and
management of the Deputy Commissioner and forest estates were Consolidated and
Demarcated.
(ii) The Period of Transition (1894 to 1903) various categories of forests were constituted
and notified under the provisions of Indian Forest Act, 1878.
(iii) The Period of Scientific Management (1903-04 to 1980-81): The forests were managed
under Regular Working Plans. The systems of management adopted during each period are
described below:
7.8.1: The Period of Organization (1846 to 1894):
This period is very significant from the point of view of Consolidation and Demarcation of the
forest estates. The forests were managed by the Deputy Commissioner on principles of simple
Forest Conservancy Rules. The Conservancy Rules contained in Barne’s Land Revenue
settlement (1849-52) asserted the exclusive right of the Govt. to sell timber, prohibited cutting
of green wood for fuel and made an order of the village head-man necessary, before felling of
trees for building purposes. The laxity of the system, however, failed to protect the forests from
98
misuse. These rules were modified by Bailey in 1853. Bailey’s Code of Rules provided for a more
stringent system of forest conservancy; the divisions of all forest lands into three more or less
equal parts to be closed in rotation for 3 or more years (i.e. trihai, the name still in use for a
closed area whether 1/3 or not); for better control in the open area; for prohibition of grass-
burning in winter and extension of cultivation without permission and for the appointment of
Forest Assistants (Ban-Wazirs) in each paragana.
In 1855 the “General Rules for Forest Conservancy in Punjab Hill Tracts” were introduced and
under its provisions Colonel Lake, the then Commissioner made certain amendments to BaiIey’s
Rules which were sanctioned by TA-Governor in 1859. These rules necessitated for Zamindars
to apply to the Tehsildar for all the timber requirements for building or agricultural purposes
and to pay a nominal fee for the same instead of getting it free by applying to the village head-
man. On the other hand the 1/4 share in the value of the timber sold annually by the Govt. was
to be awarded to the village officials and the village community; with the objective of securing
their interest and cooperation in forest conservancy. These two measures laid the foundation
of what are now called the grant of trees at Z-rate and the distribution of Z-share.
In 1859 and 1860, the trihais in each mauza were delineated and closed to exercise of rights.
Only the first trihai was marked on the ground but no arrangement was made to close the
remaining area in rotation as was the original conception. During Anderson’s Settlement the
original trihais were further notified in 1897 for 20 years closure and thus majority of areas
closed in 1860 remained closed up to 1917, i.e. for a period of 57 years. The effect of this long
closure was extremely beneficial. Adequate chil regeneration was obtained which now forms
the mature crop. The rest of the forests being inadequately protected and subjected to
increased pressure of rights for longer periods, deteriorated immensely; so much so that many
of them reached the level of extinction.
As regards commercial felling, the chil trees were sold to the traders by Deputy Commissioner
at a fixed rate of Rs. 8/- per tree. Logically only sound trees of large dimensions and from
accessible localities were rapidly removed. In case of oak and fir also the traders obtained
permits at fixed rates irrespective of the size of trees and thus only the best and mature trees
from accessible areas were removed. However, since the demand was not heavy and young
and middle aged trees were not touched the, results were not as injurious as one would expect
under the circumstances.
7.8.2: The Period of Transition (1894 to 1903):
The management of Forests was transferred to the Forest Department in 1894. The Forest
Settlements were completed and various categories of forests were constituted and notified
under Indian Forest Act. The old system of management continued more or less unchanged.
However, a system of Improvement Felling bearing on all classes in accordance with the silvi
cultural requirements of the crop, was introduced in chil forests.
7.8.3: The Period of Scientific Management (1903-04 to 1980-81):
During this period most of the forests were managed under successive Regular Working Plans.
These are discussed below:
7.8.4: HART’S WORKING PLAN (1903-04 TO 1920):
The main objects of management were to bring the whole workable area under regular
treatment, to provide for realization of sustained annual yie1d; primarily for the satisfaction of
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the legitimate requirements of right holders and the surplus if any, to be sold. A total area of
46,708 ha (including areas presently in Una, Hamirpur and Palampur Forest Divisions) was
considered workable and dealt with accordingly. Seven Working Circles were constituted.
7.9.1: The Pine Working Circle:
A system of “Improvement felling and thinning” was prescribed on a felling cycle of 20 years.
Each tehsil constituted one felling series. Exploitable girth of 2m corresponding to 90 years of
age was fixed. Felling was in arrears till the middle of the plan. The position improved
subsequently when traders were allowed to fell large sized trees. This resulted in removal of
trees of higher classes from all over the area but dense young crop in need of thinning was left
untouched. The position somewhat improved when special thinning were made by marking
trees to right holders.
7.9.2: The Scrub Working Circle:
A system of “Coppice with Standards” with a rotation of 20 years was prescribed, 25 standards
per acre were retained. As practically there was no demand, no definite sequence of felling was
thus laid down. In 1907 however, some demand arose when some trihais were worked wholly
or partly.
7.9.3: The Oak Working Circle:
A system of “Coppice with Standards” on a rotation of 25 years was prescribed. 25 standards of
oak and 50 of sal were to be retained per acre. DP Dhalun was worked, but DP Andhretta and
Kandhari & Trihais of Palampur tehsil were not at all touched.
7.9.4: Other Working Circles:
These were worked on “Selection System”. In oak high Forest Working Circle and the Fir
Working Circle no felling took place for want of demand. In Deodar Working Circle due to
limited demand only 66% of the selection trees were removed.
7.9.5: Results:
On the whole the Results of Hart’s Working Plan was satisfactory. Many of the prescriptions
could not be carried out due to lack of demand. The chil forest improved by thinning and by the
removal of over mature stock, generally of poor quality. Hart’s Working Plan did not actually
expire till 1922-23 but poor progress of chil regeneration and introduction of scheme of
Rotational Closure made its early revision imperative.
7.10: SCHEME OF ROTATIONAL CLOSURE BY MITCHELL AND WALTER (1919):
The back ground of the scheme has been dealt in para 31 above. The details of the scheme are
to be found in the special report submitted to the Govt. by Mitchell and Walters in 1919
(Report on delineation of areas to be subjected to scheme of Rotational Closure in Kangra
proper). The Delimited Protected Forests (subjected to the scheme) were divided into a number
of closure series. Each Closure series in chil, oak and fir forests was divided into 4 parts to be
closed in rotation for 30 years while in case of scrub forests each closure Series was divided into
3 parts to be closed in rotation up to 10 years. The first closures were marked on the ground
and sequence of other closures was shown on the maps and kept in a bound register called the
English register. The internal boundaries of the closures, though subject to slight modification in
particular cases, are binding. The sequence of closure is at choice only in cases where the
Zamindars exercising rights in the closure series in question are unaffected by closures in other
series. However, in the case of and forests of chakban tikas of Boh, Drini, Kareri ,Dharamshala
and Khaniayara the conditions were to be exceptional. They contained vast areas above tree
100
line in the form of Alpine pastures. Therefore no general delimitation separating such area from
the workable forests was undertaken and also in order to avoid distrust only the first closure
delineated on the ground.
7.10. 1: The Govt. accepted the scheme in 1921 and ordered that in every case where the
closure of more than 1/3 of scrub forest and 1/4 of other forest was contemplated, the
Commissioner should satisfy himself that the areas left open were adequate to the use of the
people.
7.10.2: Results:
The Rotational Closure Scheme provided satisfactory solution to the problem of selection and
notification of closures so far as the Delimited Protected Forests were concerned, but at the
same time it increased the risk of destruction of forest not included in the delimitation. In terms
of forest management the scheme in case of high forest resulted in a system of fixed periodic
blocks with regeneration period and rotation of 30 and 120 years respectively. In case of scrub
forests in fact 10 years closure was considered sufficient, which in fact was not justified.
7.11: WALTERS REVISED WORKING PLAN (1920-21 TO 1929-30):
It dealt with Reserved and Delimited Protected Forests and made general provision for 89.675
ha of Un-delimited Protected Forests. Hart’s Oak Working Circle and Scrub Working Circles
were included under one Coppice Working Circle, the Deodar and Fir, Working Circles were
amalgamated into one Circle and named Unworkable Scrub Working Circle comprising of
unworkable Delimited Protected Forests.
The objects of management in all the high forests were replacement of the irregular crop by
even aged crops normally spread over 4 age classes, maintenance of trees of all age classes in
each block of forest forming a complete closure series for the satisfaction of rights, realization
of maximum sustained yield and of maximum revenue from the surplus yield after meeting the
demands of right holders. The results of management were:
7.11.1: The Kangra Pine Working Circle:
Uniform system with artificial regeneration was prescribed. The first closure of each closure
series was allotted to PBI. Subsidiary felling with the aim of removing over mature trees
standing over pole crop along with removal of other trees in accordance with silvicultural
principles were prescribed in the other PBs. Only 50% of PBI area was subjected to regeneration
felling while only about 25% of the felled area could be regenerated. Most of the regeneration
was obtained by natural means.
7.11.2: The Coppice Working Circle:
The system adopted was “Coppice with Standard’ and sowing was prescribed to be carried out
irrespective of the area having been felled or not. There being no demand for the produce, a
large number of forests could not be worked and the prescriptions remained in arrears.
7.11.3: The Unworkable Working Circle:
This Working Circle included the Unworkable Delimited Protected Forests, all Un-delimited
Protected Forests for which no system of working could be proposed and the Alpine pastures
which could not be closed. Almost the entire area proposed for closure under Rotational
Closure scheme was closed and the results were beneficial. The rest of the areas were open to
exercise of rights as they continued to deteriorate.
101
7.11.4: The felling remained in arrears for want of demand and other related reasons
discussed below:
(a) The plan was prepared during the trade boom of world war-I and the boom was
expected to continue, but things proved to be wrong and there was a slump in the market
hence lack of demand for the forest produce.
(b) The uniform system was applied to all high forests without regard to terrain, crop
density and ecological status of the vegetation. The wholesale application of uniform system
coupled with the factor that many forests were already so open that regeneration felling was
not needed, resulted in prescription of yield which was beyond the actual capacity of the
forests. The data relating to increment was also not sound and therefore a high increment (over
100% in 30 years in case of Kangra Pine Working Circle) was adopted. No deduction for the
volume of mother trees was discounted. All these led to fixation of much higher yield.
(c) Soon after the plan came into effect a wide spread conflagration broke out in 1921,
which not only adversely affected pace of young regeneration in low hills but also burnt a large
number of trees which had been relied upon for much of the increment.
7.12: MOHAN’S REVISED WORKING PLAN (1931-32 TO 1950-51):
The plan dealt with all Delimited Protected Forests and some important Un-classed Forests. The
results of working of the plan were:
7.12.1: The Chil Shelter Wood Working Circle:
This Circle was comprised of better stocked chil forests of Walter’s Kangra Pine Working Circle
excluding some areas on account of poor stocking and precipitous terrain. Two felling series viz.
I and II were created. In felling series I surplus timber was to be sold to the traders while felling
series II was kept to meet the local demand. The silvi culture system was shelter wood with
fixed PBs, natural regeneration to be supplemented where required, by sowings. Regeneration
period and rotation were kept at 30 years and 120 years respectively in keeping with the
scheme of the plan came into effect regeneration period of 10 years had already expired, hence
regeneration of all PBI areas had to completed within the next 20 years i.e. up to 1950-51.
Mohan prescribed closure of all PBI areas at once for 20 years without waiting for seeding
felling presumably on the erroneous view that chil in the tract did not require heavy opening
for inducing regeneration and that only 25% of the area had been regenerated in Walters Plan.
About 80% of PBI area was un-regenerated. Most of the un-regenerated areas were in the
unstable sub type and being invaded by scrub. Fires also added to the difficulty of obtaining
regeneration.
The yield in PBI was in excess by about 17% at the end of the plan. The excess was essentially
due to conservative estimates of yield (two I class trees were prescribed to be left in PSI as fire
insurance at the end of regeneration period) and the forest fires which necessitated removal of
burnt tree. However the general condition of PBI areas was fairly satisfactory and the excess
yield had not exhausted the growing stock.
No felling was prescribed in PB II In PB III and IV thinning and improvement felling on very
conservative lines were prescribed, yield was to be controlled by area. In a number of forests
thinning could not be done due to lack of demand and also because of prescribed “tikawar”
system of thinning that required thinning of 1/10 of forest in each tika annually which was
found to be impracticable. However, due to heavy demand of chil poles in World War-II, all the
arrear felling were made up. The results were satisfactory on the whole.
102
7.12.2: The Coppice Working Circle:
The forests allotted to this Working Circle were mostly scrub type. Two felling series
Merchantable and Un-merchantable were created with the provision of transferring areas from
the later to the former in case of subsequent demand. The system prescribed was “Coppice
with Standed.” About 50-75 standards per ha were to be retained. Rotation of was fairly
satisfactory and the excess yield had not exhausted the growing stock.
30 years for coppice and of 90 years for standards, keeping the Rotational Closure Scheme in
view, was fixed. The yield was prescribed by area. There was a steady demand for firewood
during the period especially due to outbreak of World War-II and establishment of Yol and
other camps in the valley. The felling was therefore carried out as prescribed except in a few far
flung areas. The felling resulted in vigorous coppice shoots but regeneration by seed was
generally lacking. On the whole the prescriptions worked satisfactorily for this Working Circle.
7.12.3: The Selection Working Circle:
Forests generally situated on precipitous slopes and those which could not be close due to legal
problems were allotted to this Working Circle. Three felling series viz. (i) Merchantable
consisting of Workable areas (ii) Un-merchantable comprised of areas considered Un-workable
for want of demand and (iii) Un-classed, consisting of Un-classed Forests of the Circle where
closure could not be enforced without consent of the right holders.
The system prescribed was “Selection System” combined with thinning with felling cycle of 10
years. The yield for the first and third felling series was prescribed by number of trees for the
whole plan period instead of annual. About 50% of the I class trees prescribed for felling were
removed. The deficit was however, due to lack of demand. In the areas closed to grazing good
amount of regeneration was obtained while in others it was completely absent.
7.12.4: The Protection Working Circle:
This Circle comprised of heterogenous mixture of species in all categories of forests. Four felling
series viz. (i) Reserved Felling series comprising of Reserved Forests (ii) Tricennial (iii) Decennial
Closure felling series comprising of Delimited Protected Forest according to the closure period
of 30 and 10 years respectively and (iv) Un-classed Felling series consisting of the Un-classed
Forests were constituted. The main object of management was protection against erosion and
denudation. The Closure were prescribed in accordance with legal status of the forests and the
provisions of the Settlement. No felling and thinning were prescribed. Extensive chil sowings
were prescribe but could be carried out only on a limited scale. Chil regeneration established
itself in favourable localities while in other areas there was an increase in the proportion of
scrub. The object of forming this Circle was very well achieved; the blanks were covered with
vegetation of one type or the other. The process of erosion was checked and the general
condition of soil improved considerably.
7.12.5: Summary of Results of Mohan’s Plan:
The prescriptions and suggestions of various Working Circles were almost fully implemented.
Shelter wood System introduced by Walter in 1921 and continued in this plan for Chil and
Oak, proved suitable. In all working Circles natural regeneration was adequate and fairly
good, artificial regeneration was also obtained. The demands of right holders were fully met
with. Felling except in Chil Shelter wood Working Circle, were only slightly behind the
schedule and proved beneficial to the crop. A large number of buildings, roads and bridle
paths were constructed. Deodar was artificially introduced though on a limited scale, in
103
comptt 3 of D.P. Dharmkot, DP Chakbar. Kareri comptt 5, P. 42. K Leondnal comptt I. It has
done very well in case of D.P. Dharmkot and Chakban Kareri while in Leondnal it has failed.
7.13: REVISED WORKING PLAN BY ROMESH (1950-51 TO 1980):
All the delimited Protected and some important and valuable Un-classed Forests except those
transferred to Kangra Cooperative Forest Societies were dealt with in this plan. For Kangra
Forest Cooperative Societies separate working plan, as discussed below was prepared. The
different Working Circles are discussed as under
7.13.1: The Chil Shelter wood Working Plan:
This Working Circle contained better stocked and economically more important chil forests. In
addition to the forests of Chil Working Circle of Mohan’s Plan some chil areas of Protection
Working Circle considered better stocked were also included. The Silviculture System adopted
was “The Punjab Shelter wood System” with reliance placed on natural regeneration
supplemented by artificial means at lower elevations. Rotation of 120 years and regeneration
period of 30 years in keeping with the scheme of Rotational Closure was followed. The first
period of closure commencing in 1921 had expired on 31 March 1951 and the second period of
3 years, started on 1st April, 1951, the regeneration was to be completed in all PB I areas by
31st March, 1981. Most of the PB I areas were closed in 1951. The control of yield was by
volume. Seeding felling was to be completed within the first 10 years, of the Plan. No sequence
of felling was, however, laid down.
During the period 1951-52 to 1965-66 when this plan was revised by Malhotra, an area of 943
ha against a total prescribed area of 1622 ha (for the entire tract dealt with in the plan); that is
about 60% was felled, whereas excess yield of 3668 m3 against a total of 54,600 m
3 (for 15
years) that is about 7% of the totá1 was removed. Out of 2230 ha PB I area only 259 ha could
be regenerated fully and 140 ha moderately. In the remaining area regeneration did not keep
pace with felling. No felling was to be done in PB II. In PB III only thinning was to be done and in
PB IV felling of the remaining seed bearers along with cleaning and thinning were to be carried
out. Both these operations, however, remained in arrears.
7.13.2: The Coppice Working Circle:
This Working Circle comprised of fully stocked, better type scrub forests. This Working Circle
was same as in Mohan’s Plan except that few better areas protection. Working Circle which had
improved were also include The silviculture system continued to be “Coppice with Standard”
retaining 50 standards per ha Coppice rotation was 30 years and for standards it was 90 years.
Yield was prescribed by area, being 1/10 of each closure series.
7.13.3: Each compartment was divided into 10 coupes which caused much difficulty in correct
demarcation of annual coupes on the ground resulting in complaints from the purchasers.
Closure and regeneration of such small coupes was also a problem. Felling could not take place
as contemplated due to coupes not being sold for their size being too small. About 80% of the
prescribed area was felled. Eucalyptus introduced in the felled areas proved initially successful
but lagging in height and diameter growth later on, resulting in discontinuation of eucalyptus
planting from 1966 - 67 onwards.
104
7.13.4: The Selection Working Circle:
This Working Circle was comprised of Delimited Protected and Un-classed Forests situated on
steep and broken grounds containing an irregular crop of heterogeneous mixture of various
species. The silvi culture system adopted was “Selection System” combined with thinning.
Exploitable diameter was kept at 60 cm dbh for all species. A felling cycle of 10 years was kept.
Reliance was essentially on natural regeneration. The yield was prescribed by forest for the
entire plan period and was 33% of selection tress (I class trees). Felling of trees below 60 cm
dbh was controlled by felling rules but no yield was prescribed from such trees.
Almost all the areas due for felling up to 1965- 66 were gone over and the crop improved
markedly. However, the regeneration did not come up as expected for want of closure.
7.13.5: The Protection Working Circle:
This Working Circle included those Delimited and Un-classed Forests in which the object of
management was simple protection for checking their steady deterioration and to improve the
condition of growing stock The vegetation included all sorts of species like chil, oak, fir, spruce
etc. along
with alpine and sub alpine pastures. Density of the crop without doubt was very poor, blanks
most common and the ground was precipitous with frequent landslips. Like in Mohan’s Plan 4
felling series were constituted.
No specific silviculture system was followed. No felling consequently was prescribed except for
meeting the demand of right holders. The trees to right holders were to be marked on very
conservative selection felling and thinning. Artificial regeneration of chil, khair, shisham, oak
etc. was prescribed for suitable sites. The areas were in fact merely closed where little efforts at
artificial regeneration were made. From 1962-63 to 1965-66 some suitable areas were planted
with eucalyptus after clear felling. The growth and development of eucalyptus having not been
found satisfactory, further attempts of eucalyptus planting were abandoned.
7.13.6: The Plantation Working Circle:
This Working Circle was created in 1965-66. A felling and plantation programme was drawn up.
The forests allotted to this Circle were to be worked on “Clear felling System” followed by
plantation of chil, khair, bamboo, eucalvptus etc depending upon the soil and other factors of
the locality.
The allotment of areas to this Working Circle, was done haphazardly ignoring site conditions.
Some areas of Protection Working Circle, though unfit for clear felling were also allotted to this
Circle. Stress was laid on eucalyptus planting which generally was not suitable for the tract on
account of shallow soil and very deep water table.
105
7.14: MALHOTRA’S REVISED WORKING PLAN (1966-67 TO 1980-81):
Even though Romesh Plan was to expire in 1980-81 with the provision for interim revision after
I5 years the reorganization of the Division coupled with the desirability of bringing vast Un-
delimited Protected and Un-classed Forests under regular management necessitated complete
revision of the plan from 1966-67 itself.
The revised plan included all the Delimited Protected, Un-delimited Protected and Un-classed
Forests of the Divisions, except those under Cooperative Forest Societies. The following WCs
were constituted:
1. The Chil Shelter wood Working Circle.
2. The Oak Shelter wood Working Circle.
3. The Coppice Working Circle.
4. The Khair (Overlapping) Working Circle.
5. The Plantation Working Circle.
6. The Avenue Working Circle.
7. The Protection Working Circle.
8. The Grazing (overlapping) Working Circle.
The discussions here below are confined to forest areas falling in Dharamshala and Dehra (Part)
Forest Divisions, and the data has accordingly been presented. However, in some cases it was
felt appropriate not to split the figures and to present them in totality for the erstwhile Kangra
Forest Division as a whole dealt with under Malhotra Plan.
7.14.1: Excepting oak, Khair (Overlapping) and Coppice Working Circles the remaining Working
Circles were divided into two felling series. Felling series I (Legal Closure felling series) covered
Reserved and Delimited Protected Forests whereas Felling series II (voluntary closure Felling
series) comprised of Un-delimited Protected and Un-classed Forests. Critical appraisal by
Working Circles is discussed below:
7.14.2: The Chil Shelter Wood Working Circle:
An area of 14680.58 ha under all the 4 classes of forests of the Divisions was on the whole
under stocked, irregular, poor in growth and burdened with rights of users. The Un-delimited
Protected and Un-classed Forests brought under regular management for the first time, had
been in bad shape in the past. The area under felling series I was 6155.53 ha and 8525.25 ha in
felling series II. The main object of management was to convert the irregular chil forests into
more or less regular crop. Complete enumeration of chil in PB I of felling Series I and Felling
Series II was done. The average growing stock per ha was 64.52 m3/ha in felling series I and
51.59 m3/ha in felling series II.
The forests were to be managed under “Punjab Shelter wood System” with natural
regeneration to be supplemented by planting where ever needed. Compact groups (density not
less than 0.5) of well grown poles up to 35 cm dbh of at least 0.2 ha in extent were to be
retained as advance growth. Rotation of 120 years and regeneration period of 30 years was
adopted. In felling series I, allotment to all the 4 P.Bs. was made while in felling series II only the
PBI area were specifically allotted and the rest were grouped together under PB Others.
Only two regeneration felling, viz seeding and final felling were to be carried out when the
regeneration was at least 2m high and the area control-burnt twice. In case of PB II no felling
except for the removal of fallen, dead and dry trees was prescribed. In PB III thinning and in PB
106
IV removal of remaining over wood along with thinning in the congested groups was
prescribed.
The yield was prescribed by volume and calculated separately for PB I and PB I V of each felling
series. The control of thinning in PB III and PB IV was by area. PB Others of felling series II was
meant only to meet the right holders demand and thus no yield was prescribed. Yield from P.B.
was calculated by deduction from the existing growing stock of the trees of 20 cm dbh and up
the volume of seed bearers and advance growth to be retained as part of the future crop.
Though annual yield was calculated, no annual control was to be exercised at the end of the
plan. All trees of IV class and above from PB I and all trees III class and above removed under
salvage felling in PB II were to count against the yield of FS-I. Sequence of seeding felling and
final felling (for Felling Series I) were prescribed. Main yield from PB IV was calculated on the
basis of percentage of I and II class trees available for felling.
7.14.2.1: Results of Working:
The position of yield in each P.B. as on 31.3.1981 including the present Palampur FD is as under:
Periodic Block Excess/Deficit(m3)
I (+)24,833
II (+)5,754
III (-)411
IV (-) 17
7.14.2.2: In PB I of felling series I, an area of 722.73 ha was prescribed for Seeding/ corrective
felling. All the prescribed area was felled. Similarly final felling prescribed over 164.70 ha was
duly carried out within the plan period.
7.14.2.3: In the felling series II against an area of 1170.28 ha prescribed in PB I for seeding
felling only 102.76 ha was felled and 1067.52 ha remained in arrears because of excess felling
under salvage removals.
Table 43: AREAS PRESCRIBED BUT NOT FELLED: U 4 D Khariana C2 7.69 UP149 K Romehar 1 5.67 U 5 D Kandhwar 1 10.52
C14 23.07 U 6 D Tihri 2 33.19 8 44.51
C16 16.19 U 7 D Majhin 26 17.40 U 3 0 Habrol 2 40.06
U I D Bilaspur C4a 55.84 28 18.21 7 20.23
U 2 D Larol 1 12.55 33 30.75 21 25.90
UP 139 K D’sala 9 23.88 UP 137 K Drini I C2 21.45
16b 20.23 UP 98 K Marhun W 8.90
UP 23 K Paid W 22.66 UP 99K Gobarnand 1 25.09
UP 24 K Sehwan 1 16.19 2 17.00
UP 28 K Khola 1 18.62 UP106K Boharkwalu 1 6.07
UP29 K Borusarna 1 46.53 U 8 D Kuthialta 1 46.94
UP 42 K Chulahan 1 12.96 Up 8 D Mhadev 13 51.39
UP 70 Khola . 1 24.28 Up 137 K Drini II 10 52.60
UP 149 K Chari 2 22.66 12 25.90
4 61.50 13 40.06
UP 144 K Sakoh 8 6.07 UP I D Ghalaur 2 25.09 TOTAL 1067.52
Against a prescribed area of 2057.71 ha in PB I in the felling series II, only 990.19 ha area was
felled leaving 1067.52 ha un-felled. That means 51.87% of the area remained un-felled, yet
there has been a plus deviation of the order of 24,833 m3.
107
7.14.2.4: There is excess removal of about 60% of the total prescribed yield in PB I of both the
felling series. It is said that the plus deviation in PB I is mainly for the reasons of heavy salvage
removals carried out year after year of the fire burnt, dry, dead, fallen etc trees. To a fair
degree this assumption might be correct but not wholly true. It is felt that yield calculations
done by Malhotra were not sound and the yield calculated was much on the conservative side,
as is discussed hereafter:
(i) The annual increment worked out on the basis of increment percent, in felling series I came
to 9735 m3 against which yield of only 370m3 was prescribed (2780 m3 for PB I and 1000 m3
for PB IV) and all removals including removals by right holders were to count against this yield.
Hence very low yield was prescribed while removals were much heavier.
(ii) In accordance with para 90.1 of Malhotra’s Plan, volume of 29 trees ( IA &over/4, IIB/6,
IIA/11,III/4, IV/4) had been deducted while calculating yield from PB I felling series I.
Comparison of the class-wise trees actually available per ha as obtained from enumeration
figures with the number of trees prescribed for retention presents the following picture :
Diameter No. of trees prescribed No. of trees actually
Class (per ha) available (per ha)
IV 4 11.00
III 4 10.93
IIA 11 9.77
IIB 6 7.48
IB 4 4.57
7.14.2.5: From the above table it is inferred that while calculating “YieId” almost all IIA and
above trees were retained while only III and IV class trees, after deducting volume of advance
growth, were to be felled for realizing the yield. This view is not in keeping with the established
principles of seeding felling in PB I. Likewise in felling series II, 25 trees / ha of IIA and above
were retained as mother trees. The availability position of average number of trees as worked
out on the basis of enumeration data is as under:
Class No. of trees actually
available (per ha)
IV 6.23
III 8.27
IIA 7.25
IIB 5.56
IA 2.35
IB 0.93
IC 0.31
ID 0.17
7.14.2.6: From the above it is clear that only 16.57 trees per ha of IIA and above were available
white 25 trees per ha were prescribed for retention and made use of in the calculation of yield.
Almost all the IIA and above trees were retained in PB I of felling series I while in PB I felling
series II much more number of IIA and above trees were retained as were even not actually
available, resulting in removal of only the III and IV class which is a negation of the
108
fundamentals. Of seeding felling, even Romesh had prescribed retention of only 15 to 20 trees
per ha as seed bears and such is the actual practice in PB I areas. Retention of 25 to 28 trees per
ha is much too heavy. Actually retention is made only of IIA trees and sparingly of few IIB trees.
Therefore yield as calculated by Malhotra was much too conservative, hence the apparent
excess removals.
7.14.2.7: In case of PB II, no felling except for removal of dead, dry fire burnt etc trees was to
take place hence no yield was prescribed. The plus deviation is on account of no prescription
for this PB yet removal of the above mentioned categories of trees. This has led to depletion of
growing stock in PB II and is mainly attributed to the removal of fire burnt trees that dried as
a result of the faulty practice of resin tapping.
7.14.2.8: In PB III felling series I against a prescribed area of 1161.63 ha only 663.31 ha was
felled under thinning, leaving 498.12 ha un-worked; most probably on account of excess
removals elsewhere. The under mentioned are the areas that were prescribed but not felled.
P B III AREAs PRESCRIBED BUT NOT FELLED
P 39 K Ranital 3f 19.42
3e 14.67
4c 12.95
5d 14.57
P 24 K Lunj 2d 26.71
4d 20.64
p 4 K Sunkanal 2d 17.81
p 44 K CB Dulli Id 43.29
2d 13.35
R 14 D Khalag W 15.78
P 27 K Pathiar 4a 21.04
4b 24.68
P 28 K Mansu ld 7.28
P 51 K Naddi 2a 18.21
3b 32.37
P 43 K Cheli ld 42.08
Kareri 2d 4.05
3d 13.76
4c 12.95
R 3 D Habrol 2a 87.80
3d 29.14
Total 498.12
7.15.1: In PB IV felling series I, against a prescribed area of 1240.10 ha to be gone over in
thinning only 844.71 ha was felled leaving 395.39 ha un-felled. There is practically no deviation
in the yield from PB IV. The following areas were not felled against the prescriptions:
109
Table 44: PB IV AREA PRESCRIBED BUT NOT FELLED:
P 14 K CB Dulli 1a 22.50 P 24 K Lunj 1a 22.26
2a 30.25 2a 29.24
P 53 K Kalfun 1a 9.72 P 26 K
Chelighalian
4 4.05
P 45 K
Borusarna
1 73.24 P 43 K Cheli
Kareri
59 10.93
P 14 K
Pandhwar
2a 113.71 P 51 K Naddi 2a 28.83
5a 19.83 P 13 K Doda
Dwari
1 12.14
P 20 K Prgor
Kalru
1a 16.19 395.39
7.15.2: In PB I V felling series II neither felling were prescribed nor were such felling carried
out.
7.16: The status of regeneration of PB I areas of felling series I (Legal Closure) at the
beginning and also at end of Malhotra’s Plan is as under:
Status of Beginning of Pla n End of Plan
Regeneration Ha % of Total Ha % of Total
1. Advance growth 102.94 7.44 97.01 7.01
2. Completely 168.15 12.15 513.90 37.14
regenerated
3. Moderately 130.95 9.46 93.32 6.75
regenerated
4. Poorly regenerated 142.60 10.31 136.12 9.84
5. Culturable blanks 798.58 57.72 382.47 28.37
where regeneration
operationsare
afootandlikely
tosucceed.
Unculturable 40.35 2.92 150.72 10.89
blanks
Total 1382.57 100.00 1387.57 100.00
110
7.17: The status of regeneration of PB I areas of felling series II (Voluntary Closure) at the end
of Malhotra Plan is as below :
S.No. Status of regeneration At End of Plan
Area(ha) % of total
1. Advance growth 2.00 0.11
2. Completely regenerated 200.46 11.29
3. Moderately regenerated 274.71 15.47
4. Poorly regenerated 236.63 13.32
5. Culturable blanks where 817.78 46.04
regeneration operations
are afoot and likely to
succeed.
6. Un-culturable blanks 244.60 13.71
Total 1776.18 100.00
7.18: From the foregoing illustrations it can be safely realized that there has been a marked
improvement in regeneration of PB I areas of felling series I while PB I areas of felling series II
have not been satisfactorily regenerated as was contemplated under Malhotra’s plan,
essentially on account of non felling of about .91.21% of the prescribed area.
Thus in conclusion it can be stated that chil forests can be regenerated provided timely seeding
felling are carried out, strict protection against forest fires is ensured and effective closure of
regeneration areas is not allowed to be tampered with. Rotation of 120 years and regeneration
period of 30 years is well suited for chil management and no change therein is required.
7.19: THE BAN OAK WORKING CIRCLE:
It was comprised of workable Ban and Kharsu oak areas in Delimited Protected Forests of
Dharamshala Range. The forests were under stocked, badly lopped and overgrazed. The crop
was middle aged to mature and deficient in younger age classes. No enumerations were carried
out and enumeration figures of Romesh Plan were made use of.
7.19.1: The objects of management were protection and preservation, introduction of valuable
species like chill etc on suitable sites for obtaining maximum yield of firewood and charcoal
and to meeting needs of the local population for fodder and grazing. The forests were to be
managing under Pun jab Shelter wood System with artificial regeneration. Rotation of 120 and
regeneration period of 30 years was adopted. PB I and PB I V areas were definitely allotted and
the remaining forests were lumped together under P.B. Un-allotted. In PB I, two fellings viz
seeding and final fallings were to be done. 25 to 40 trees per ha were to be retained as mother
trees. Compact groups of poles of 40 cm dbh and below but not less than 0.2 ha extents were
to be retained as part of the future crop. Final fallings were to be carried out when young crop
was at least lm in height.
7.19.2: The main yield was calculated in terms of charcoal equivalent. The intermediate yield
from PB IV was regulated by area. 16.19 ha of Dharamshala Range were not felled under
seeding felling during the plan under revision. The position of yield of PB I as on 31.3.1981 was
that it was (-) 22,559.6O qtls. The deficit yield is because more than 50% of the prescribed area
remained un-felled.
111
7.19.3: In P B IV an area of 252 50 ha was prescribed for felling against which only 110.47 ha
area was gone over leaving 142.03 ha as un-felled. Thus about 56% of area remained un-felled
obviously for two reasons; firstly for imposition of ban on oak felling clamped by the Govt. and
secondly on account of uneconomical working of these forests.
7.19.4: PB IV Areas Prescribed but not Felled:
P 40 K CB Karen C3a 104.39
P 41 K Kutharna cl 37.64
142.03
The yield position of P. 13 IV as on 31.3.1981 was (-) 151.91 ha
As per sowing/planting programme 284.89 ha was prescribed against which only a very small
area was planted with ban, realistic figures not being available. Status of regeneration of PB I
areas is given below:
Status Area (ha) % of the total area
1. Fully regenerated 121.93 42.80
2. Partially regenerated 26.72 9.38
3. Culturable blanks where 28.23 30.97
Regeneration operations
Are afoot and likely to
Succeed,
4. Unculturable blanks 48.01 16.86
283.89 100.00
7.19.5: From the above table it is inferred that only less than 50% of the area has been
regenerated when regeneration period of 30 years has ended. The reason is lack of sincere
efforts on the part of the staff. Provided due protection is given, ban oak regeneration is not a
problem as the locality factors do not pose any silvicultural or ecological difficulties and are in
fact favourable.
7.20: THE COPPICE WORKING CIRCLE:
All the better stocked forest as distinct from scrub areas, were allotted to this Circle. All the
areas of this Circle were Reserved and Delimited Protected Forests. The Silviculture System
adopted was Copice with Standard where rotation for Standards was kept at 90 years and 30
years for Coppice.
7.20.1: The yield was controlled by area. 40-50 as standards per ha were prescribed for
retention for seed production and for yielding timber of higher sizes, economically important
species like Dalbergia, Anogeissus, Aibizzia etc were suggested for retention as standards.
649.88 ha area was prescribed for felling during the plan period out of which all the prescribed
area was felled. The deviation as on 31.3.1981 was (+) 101.91 ha which is not much on the plus
side.
Sowing and plantation of khair was suggested over 229.82 ha, of which all the area was
planted- up.
112
7.20.2: The prescriptions of the Circle have almost been carried out resulting in improvement
of crop. The silviculture System adopted has been found suitable and no change therein is
warranted.
7.21: THE KHAIR (OVER LAPPING) WORKING CIRCLE:
The Circle overlapped khair bearing areas of other Working Circles, in Shahpur, Kangra and
Jawalamukhi ranges. The objects were to harvest the mature and over mature stock of khair, to
realize maximum revenue and to increase proportion of khair in suitable localities by natural
and artificial means. Khair enumerations were done in 5 cm diameter classes. No definite
silviculture system was adopted; however, exploitation of khair was prescribed on selection
principles. Exploitable diameter was kept at 25 dbh and felling cycle of 15 years was adopted.
7.21.1: For convenience of working, mauza was taken as the annual working unit. Yield was
regulated by area and number of khair trees to be removed annually. Annual removal of khair
trees was kept at 1000 trees equivalent to 950 m girth, sufficient for running of 4 katha
bhatties. 25% variation was permitted provided cumulative excess did not exceed 1000 trees
during the plan period.
7.21.2: The deviation on 31.3.1981 was (-) 2399.56 ha except for mauza Darang, Ghalaur,
Sadun, Thana, Balol and Khola all the other areas were worked as prescribed. These areas were
probably not worked owing to the trees being scattered and uneconomical to work. The non-
working of these areas explains the minus deviation satisfactorily. The prescription of the Circle
has thus been followed and objects of management set out achieved. No change in the
management practice is called for.
7.22: THE PLANTATION WORKING CIRCLE:
The areas which were under stocked, stocked with inferior brushwood species or with large
culturable blanks were alotted to this Working Circle. The legal and voluntary closure felling
series were constituted, as discussed in earlier Circles. The objects of management were to
clothe the blank areas and replace inferior scrub forests with economically valuable plantations
and to nurse and maintain the existing stock.
7.22.1: The modified clear felling with artificial regeneration was adopted as the silviculture
system. About 35-40 standards were to be retained per ha for providing seed, shade and large
sized timber etc. no felling of chil unless diseased, dry or wind fallen was to be done. Khair trees
below 15 cm dbh were not to be felled. In felling series II, no commercial fallings were
prescribed. Here the felling was confined only to meeting the demand of right holders. Bamboo
was also prescribed for planting in fertile pockets of the low lying forests.
7.22.2: In felling series I an area of 1105.95 ha was prescribed for felling and planting and
877.48 ha was laid down for closure and planting where no felling were needed. Against these
prescriptions except 84.57 ha area which could not be felled, rest was felled and planted up. In
felling series II plantation programme for 2211.99 ha was laid down. All the prescribed areas
have been planted up with chil, khair and other misc B.L. Spp. In fact the plantation targets laid
down have greatly been exceeded. Thus the position of working of the circle has been
satisfactory. No change of silviculture system is called for as it has given good results. What is
now required is that emphasis should be not only on species like chil and khair but should
include other species yielding fodder, fuel, fruit, small timber etc. for catering to the needs of
local population.
113
7.22.3: Subsidiary silvicultural operations like bush cutting, weeding, cleaning, thinning and
other regulations regarding closure and grass cutting were generally carried out as suggested.
However, in some chil plantations bush cutting cleaning and pruning were not carried out
which resulted in severe damage by forest fires.
7.23: THE AVENUE WORKING CIRCLE:
The P.W.D. roadside strips and the strips of land along railway—tracts were allotted to this
Working Circle. These strips contained young to mature B.L. trees. The crop was patchy, open
and irregular with large blanks. There was hardly any restriction on grazing, lopping, debarking
and other damage. One felling series for the P.W.D. road side strips and the other for railway
strips were constituted. The growing stock in both the felling series was much lower than the
normal. Position of regeneration was unsatisfactory. The main objects of management were to
restock the blanks with species valuable from aesthetic and economic considerations. The main
species to be planted were Cassia siamea, Jacaranda ovalifolia, Grevillea robusta, Bauhinia
variegata, Harsingar,Mango, Gulmohar etc. No definite silvicultural system was prescribed.
However, removal of dead, dying, diseased trees causing hindrance to smooth flow of traffic
were allowed to be removed.
Planting programme for the two series was laid down. 307 km road side strips and 162 km
railway strips were prescribed for planting. Other operations like fencing weeding, watering etc.
were also prescribed. The work on planting of road side strips and of the railway strips has not
been done as prescribed for various administrative and management reasons where only a
fraction of the prescribed length was planted up.
7.24: THE PROTECTION WORKING CIRCLE:
This Working Circle includes all types of unworkable forests situated on very difficult and
precipitous slopes or at other erosion prone sites like banks of nallas and streams. High level
pastures and other blank areas where soil is absent or is negligible and no planting works could
be done, besides the forests being in-accessible and burdened with rights of grazing were
allotted to this Working Circle. Protection of hill sides from denudation and erosion and
improvement of the growing stock were the main objectives of management. Like other
Working Circles two felling series were constituted. No definite silviculture system was
prescribed. Felling to meet the demand of local population was permitted on silvicultural
principles; Sowing/planting programme for each felling series was laid down. It was not
mandatory for the staff to stick to the areas prescribed and they could take any other area for
planting that was not included in the programme or change the sequence of planting.
Misc. regulations like closure for planting, regulating of grazing, grass cutting, lopping were also
laid down which were only partially implemented.
Most of the prescribed areas were closed and planted. The planting programme was mainly laid
down for the lower areas i.e. the scrub and chil forests and no treatment for improvement of
the crop or restocking of blanks in higher areas of ban, fir spruce and kharsu oak forests was
suggested. Irrespective of the crop density, especially in areas of felling series II, almost entire
forest compartments were prescribed for planting. Moreover planting of vast chunks was not
possible in view of difficulties of large scale closures. However, the prescriptions have generally
improved the forests of the circle both in terms of their stabilization in the face of erosion and
in bringing green cover to the open sites.
114
7.25: THE GRAZING WORKING CIRCLE:
This was an over lapping Working Circle divided into 4 zones; (1) Alpine (2) higher Zone (3)
Middle Zone (4) Lower Zone. The object of management was to provide grazing and folder for
the requirement of right holders. Assessment of the productivity of the grazing lands was done
and the detail of cattle population of the local, migratory and nomadic graziers was given. In
order to evolve a sound grazing policy measures like (i) revision of the settlement (ii)
Conversion of grazing land into ghasnies (iii) increase in grazing fee (iv)planting of fodder
species etc was suggested. Against these prescriptions a negligible area was planted with
fodder species under the pasture improvement scheme. Besides this, planting of khair and B.L.
spp over a small area was also done under plan schemes. The other suggestions could not be
implemented.
7.26: FIRE PROTECTION:
PB I areas of Chil Shelter wood Working Circle required to be control burnt at least twice, which
suggestion has not been implemented resulting in increasing number of forest fires, as is given
under para 19.1.
7.27: SPECIAL WORKS OF IMPROVEMENT:
A list of forest roads paths with their year of construction has been given as appendix XVI. Many
km of bridle path/Inspection path were constructed during the plan period. However, all
suggestions regarding constructions of roads and paths have not been implemented probably
due to financial or other administrative constraints.
7.28: BUILDINGS:
A list of buildings of the year and cost of construction has been given in appendix XVI. The
repair and maintenance of old buildings, especially those in remote areas, continued to suffer
for want of funds and other administrative reasons.
7.29: FORESTS OF THE COOPERATIVE FOREST SOCIETIES:
The forests now with the Cooperative Forest Societies were managed with other Govt. Forests
prior to 1941. It was in the year 1941 when the Cooperative Forests Societies were constituted.
Before 1967-68 each Cooperative Forest Society had a separate working scheme/working plan
as detailed under:
115
Table 45: CFSs in Dehra:
S
No
Name of CFS. Author of first
W.P./ Working Sch.
Author of the second W.P./
Working Sch.
1 Dhalun Sunder Singh (1.4.41 to 31.3.61) E. S. Dass (1.4.51 to 31.3.66)
2 Gharoh Bachan Singh (1.4.46 to 31.3.61) E. S. Dass (1.4.61 to 31.3.76)
3 Ghurkari Arjan Singh (1.4.42 to 31.3.52) E.S.Dass (1.4.52 to 31.3.67)
4 Khaniyara Gurdas Mohan (1.4.45 to
31.3.60)
-----
5. Kholi Gurdas Mohan (1.4.49 to
31.3.61)
---
6. Sarah Jogdhian (1.4.46 to 31.3.61) E. S. Dass (1.4.53 to 31.3.81)
7. Sudhed Bachan Singh (1.4.46 to 31.3.61) Agea Ram (1.4.61 to 31.3 .76)
8. Sidhbari Jogdhian (1.4.49 to 31.3.69) ---
9. Sukar Maqbul Ahmed (1.4.47 to
31.3.62)
Malik (1.4.65 to 31.3.80)
10. Thana Jogdhian (1.4.49 to 31.3.59) ---
11. Yol Jogdhian (1.4.49.to 31.3.69) ---
12. Bari Han Singh (1.4.45 to 31.3.60) Agea Ram (1.4.60 to 31.3.75)
13. Danoa Gurdas Mohan (1.4.41 to
31.3.51)
E.S.Dass (1.4.51 to 31.3.66)
14. D-Gopipur Gurdas Mohan (1.4.45 to
31.3.60)
Agea Ram (1.4.60 to 31.3.75)
15. Erla Gurdas Mohan (1.4.41 to
31.3.51)
E. S. Dass (1.4.51 to 31.3.69)
16. Gumber Gurdas Mohan (1.4.44 to
31.3.54)
Ram Parkash (1.4.45.to
31.3.69)
17. Haripur Gurdas Mohan (1.4.50 to
31.3.70)
---
18. Muhl Gurdas Mohan (1.4.42 to
31.3.53)
E.S.Dass (1.4.52 to 31.3.67)
19. Paisa Ahmed Khan (1.4.44 to 31.3 59) ----
20. sanot Gurdas Mohan (1.4.45 to
31.3.60)
Agea Ram (1.4.60. to 31.3.75)
21. Tatahan Khurd Mohinder Singh (1.4.52 to
31.3.67)
----
22. Trippal Bachan Singh (1.4.46 to 31.3.61) ---
23. Behnala Sunder Singh (1.4.41 to 31.3.51) E. S. Dass (1.4.51 to 31.3.66)
24. Dobh Bhagwan Singh (1.4.51 to
31.3.51)
---
25. Manjgraon Gurdas Mohan (1.4.49 to
31.3.71)
---
26 Salol Mohinder Singh (1.4.51 to
31.3.66)
---
116
7.30: RAWAL’S INTEGRATED WORKING PLAN (1968-69 TO 1982 -83):
The first Integrated Working Plan for the Cooperative Societies of Kangra district was compiled
by Rawal for the period 1967-68 to 1982-83. There were 29 Cooperative Forest Societies in
Dharamshala and Dehra (Part) Forest Division. The following Working Circles were recognized
by him:
(i) The Chil Working Circle (ii) The Oak Working Circle (iii) The Fuel and Fodder Working Circle
(iv) The Coppice with Standards Working Circle(v) The Bamboo Working Circle (vi) The
Plantation Working Circle
(vii) The Protection Working Circle
The working of each circle is discussed below in brief. However, for details, a reference is
invited to Rawal’s plan.
7.30.1: Chil Working Circle:
An area of 849.74 ha was covered under this Circle of which allotment to each periodic block
was as below:
PB I PB II PB III PB IV Total
208.39 208.43 180.86 252.06 849.74
The system and the principles of management were generally the same as in the Romesh Plan
already discussed save for one salient variation that yields here was regulated by area in place
of vo1ume.
In this Working Circle against a prescribed area of 571.22 ha, 490.45 ha was felled and only
81.27 ha remained un-worked. Details of area prescribed and felled by periodic block is as
below:
P.B. Prescribed (ha) Felled (ha)
I 132.33 114.12
III 210.39 185.74
IV 229.00 190.59
571.72 490.45
The prescriptions of the plan were thus carried out almost entirely resulting in satisfactory
regeneration of PB I areas and improvement in stoking density and condition of the crop in the
remaining periodic blocks.
The deviation statement of the working circle as on 31.3.1983 remained thus:
P.B. Deviation (ha)
I (—) 18.21
II Nil
III (—) 24.65
IV (—) 38.41
The status of regeneration of PB 1 areas at the end of the plan is as under:
27. Shahpur Arjun Singh (1.4.44 to 31.3.69) Agea Ram (1.4.50 to 31.3.74)
28. Jhikli Kothi Maqbul Ahmed (1.4.47 to
31.3.62)
---
29. Jalot Bhagwan Singh (1.4.50 to
31.3.65)
---
117
Sl.No. Status of regeneration At the end of Plan % of total Area
1. Advance growth ----- ----
2. Completely regenerated 123.86 56.47
3. Moderately regenerated 37.66 17. 17
4. Poorly regenerated 13.93 6.35
5. Culturable blanks where 24.23 11.05
Regeneration operations
are afoot and likely
6. Unculturable blanks 19.64 8.96
Total 219.32 100.00
7.30.2: Ban Oak Working Circle:
Some of the comptts of CFS Dhalun, Shahpur, Sudhed, Khaniyara, Yol and Manjgraon were
allotted to this circle. The Indian Irregular Shelterwood System with artificial regeneration was
adopted. In suitable areas deodar was suggested to be introduced by planting. Rotation of 120
years and regeneration period of 30 years was adopted. As no enumerations were carried out,
the yield was controlled by area. In seeding felling of PB I areas, 40-50 seed bearers per ha
above 40 cm dbh were to be retained. No programme for sowing/planting was laid down.
The area allotted to the Working Circle was 242.37 ha (212.84 ha in Dharamshala Range and
29.53 ha in Shahpur Range). Definite allotment to PB I and PB IV were made while the forests
were grouped together and allotted to P.B. Unallotted. The area figures for the three P.B. were:
P.B. Dharamshala range Range Shahpur Total
PB I 63.13 6.07 69.20
PB I V 43.70 7.28 50.98
P.B.
Unallotted 106.01 16.18 122.19
912.84 29.53 242.37
Against an area of 105.20 ha prescribed for felling; 94.28 ha were worked, leaving only 10.92 ha
un-felled. Area figures by PB are:
PB Prescribed (ha) Felled (ha)
I 54.22 48.15
IV 50.98 46.13
Total 105.20 94.28
7.30.3: The Bamboo Working Circle:
As no areas of Dharamshala and Dehra (Part) Forest Divisions were allotted to this Working
Circle in the plan under revision, working of the circle is not discussed.
7.30.4: The Coppice Working Circle:
118
All the better type miscellaneous and scrub forests were allotted to this Circle. The system of
management was coppice with standards, with Rotation of 90 years for standards and 30 years
for coppice. 40-50 vigorously growing trees of valuable species per ha were to be retained as
standards. Other valuable species like chil, mango and young growth of economically valuable
species were to be retained. As area of 820.99 ha was prescribed for felling in the shape of
annual coupes over the plan period of this 745.78 ha was felled and 75.21 ha remained
unworked. Definite programne of sowing/planting was not laid down. However,
sowing/planting of species like chil, khair, shisham, Eucalyptus and siris was recommended.
The prescriptions of the circle have worked well and density of stocking has considerably
improved. The rotation age for coppice and standards fixed at30 and 90 years respectively is
suitable and no change therein is required.
7.30.5: The Plantation Working Circle:
Allotted to this circle were the areas with deep and fertile soil but which were either blank or
were largely overgrown with useless scrub such as Mallotus, Carrissa, Dodonaea, Murraya etc.
No definite silviculture system was adopted. No sequence of felling was either needed or
prescribed. The areas were to be clear felled and sown/planted with chil, khair, mango,
shisham, bamboo.
1397.70 ha area (813.90 in Dharamshala, 402.80 in Jwalamukhi and 181.00 ha in Shahpur
Range) was prescribed for sowing/planting during the plan period. Out of this more area was
planted up than that prescribed. On the whole the prescriptions have done much good to the
areas allotted to this circle and substantial plantations have been raised. The Working Circle
needs to be continued.
7.30.6: The Fuel and Fodder Working Circle:
All the denuded and serni denuded type of scrub forests adjoining habitations and which were
mostly used for meeting every day needs of life like fuel, fodder, wood for agriculture system
was adopted. Similarly no rotation age or exploitable diameter was fixed. No yield was
prescribed. The areas allotted to this circle were to remain open for meeting every day needs of
local population and to be used as grazing grounds. Rotational Closure of half of the available
area to grazing was suggested to be implemented on voluntary basis by the concerned society
and the remaining half to remain open. Certain guidelines to be enforced strictly for lopping
were laid down.
The total area of the circle was 3534.19 (Dharamshala 2075.60 ha, Jawalamukhi 1132.19 ha
Shahpur 325.68 ha). As no definite prescriptions were laid down, no clear results were to be
expected nor were they obtained. There is no justification for continuance of this circle. As
these areas are in bits and of small sizes, as also close to habitations and used as grazing
grounds for the village cattle, their closure is impossibility with the result they need to be
allotted to Protection Working Circle.
7.30.7: The Protection Working Circle:
This Circle was comprised of all the remaining forests not allotted to any of the above
mentioned Working Circles. No definite silviculture system was prescribed. The areas of the
working circle were to remain closed for 15 years from 1.4.1968 for the grass and tree growth
119
to flourish and spread. Programme for sowing and planting of chil and khair was laid down for
1591.60 ha Against this prescription hardly any area has been sown/ planted.
Khair felling in Jwalamukhi Dehra and Mallan Ranges over an area of 483.84 ha area were
prescribed. Out of which 439.73 ha area was felled. Thus prescriptions of 15 years closure of all
areas from 1968 and sowing/planting over 1591.60 ha have not been followed.
7.31: GENERAL for CFSs:
(i) Control and Record: Maintenance of CFS CH files is extremely poor. Entries of felling,
planting, cultural operations, maintenance of boundary pillars etc are not available and
wherever found are far too patchy and incomplete.
(ii) State of boundaries: The boundary pillars at most places are in a state of utter disrepair
and at some places altogether missing. The programme of repairs to boundary pillars has not
been properly followed.
(iii) Encroachment: Encroachment on some of the society forests are quite common. Sincere
efforts at stopping encroachments are wanting. Allotments of land to the landless have
aggravated the situation.
(iv) Fire Protection: Most of the forests particu1ally of chil have been saved from fires
resulting in good crop of young chil. However, some forests have suffered fire damage.
Defective resin tapping is the bane of forest fires and needs to be replaced by the Rill method.
7.32: CRITICAL APPRAISAL OF M.P.SINGH PLAN, (1981-82 TO 1995-96):
Right bank of the river Beas which comprises the present Jawalamukhi, Nagrota Surian and two
blocks of Dehra range (Dehra and Bankhandi) were covered under Dehra Felling Series of M.P.
Singh Plan and were worked under following Working Circles:
The Chil Shelter Wood Working Circle; The Coppice Working Circle; The Plantation Working
Circle; The Protection Working Circle; The Khair (Over lapping) Working Circle & The Wild Life
(Over lapping) Working Circle.
7.32.1: CHIL SHELTER WOOD WORKING CIRCLE:
An area of 3728.79 ha consisting of Reserved Forests, Un-demarcated Protected Forests and
Un-classed Forests and also Co-operative Forest Society forests were managed under this
working circle.
The forest of Dehra Felling Series were further divided into three inter felling series in
consonance with legal status and from management point of view: 1) the rotational closure
felling series (Felling Series-I) comprising 627.18 ha of Reserved Forests; 2) the V.C. Felling
Series (Felling series-II) included 3084.60 ha of un-demarcated Protected Forests and un-
Classed forests &, 3) the CFS (Felling Series III) contained 17.01 ha of Co-operative Society
Forests (Un-classed Forests).
The special objects of management were to continue for the conversion of generally irregular,
under- stocked chil forests to more or less regular, fully stocked pure crops. Stock mapping was
done on 1:15840 scale. General site quality was assessed to be III. Total enumeration of Chil
was carried out in 10 cm dia classes down to 10 cm dbh. The growing stock was assessed to be
113.22 m3 per ha in FS-I, 70.40 m
3 / ha in FS-II and 83.66 m
3/ha in FS-III (against normal stocking
of 160 m3/ha in normal crops). Total enumeration of Khair was also carried out in 5 cm dia
classes down to 10 cm. dbh. In general the forests were found to be under-stocked.
120
Compare with the position as of 1966-67 at the time of revision of this WP by Malhotra:
The main object of management was to convert the irregular chil forests into more or less regular crop.
Complete enumeration of chil in PB I of felling Series I and Felling Series II was done. The average
growing stock per ha was 64.52 m3/ha in felling series I and 51.59 m3/ha in felling series II.
The forests were to be managed under modified shelter wood system known as Irregular
Shelter wood System (Punjab Shelter Wood System) which permits retention of compact
groups of well grown poles upto 35 cm. dbh and not less than 0.2 ha in extent as a part of
future crop. Marking was confined to selection principles where topographical features do not
permit adoption of concentrated felling. Rotation of 120 years with regeneration period of 30
years in conformity with the requirement of rotational closure scheme was adopted. In FS I and
III definite allotment to all the PBs was made. In FS II definite allotment was made to PB I only
and remaining forests of this felling series were kept under “PB
Others”. Two regeneration felling i.e. Seeding Felling and Final felling, were to be carried out in
PB I. In seeding felling, 15 to 18 healthy, middle aged to mature Chil trees were to be retained
per ha as seed bearers. Number of seed bearers can vary upto 25 trees per ha depending upon
the topography of the area. Final felling was to be done when the regeneration was 2.5 m. in
height. Five tall, healthy and vigorously growing trees were to be retained as fire insurance. No
felling was prescribed in PB II & III. Only marking of trees in T.D. for meeting the local demand
was prescribed. In PB III & IV removal of remaining over wood along with cleaning and thinning
in congested groups of young crop was prescribed.
Yield was prescribed by volume and comprised main yield and intermediate yield. The main
yield consisted of all felling in PB I and felling of IIA and above trees in PB IV. The Intermediate
yield consisted of the cleaning and thinning in PB III, PB IV and PB others.
In FS I, total annual yield prescribed was 30000 m3 which was to be realized on annual basis as
750 m3 from PBI equal to 850m
3 (Seeding felling), PB IV 350m
3 (removal of over wood in PB IV)
and thinning, improvement felling and cleanings in PB III and PB IV equal to 800 cum3 against
which 22312.33 m3 was removed under salvage operation with a very meager volume in favour
of right holders. This removal includes 7217.44 m3 volume removed from PB II under salvage
operations against which no yield was prescribed in PB II. Deviation of + 25% in the annual yield
was allowed provided accumulative yield of 5 years did not exceed by + 10%. In PB I, yield was
calculated by adding the volume of felled trees from 1981-82 to 1985-86 and on the
assumption that 20 trees per ha will be retained as seed bearers and volume of 25% of V & IV
class trees will be retained as a part of future crop. The main yield in PB IV was calculated on
the basis of percentage of I & IInd class trees available for felling.
In FS II 63750 m3 yield was prescribed to be removed as 2100 m
3 annual yield from PB I (seeding
felling) and 2150 m3 annual yield PB others (improvement felling, thinning and cleanings) under
the plan under revision against which upto 1985-86, 1923.53m3 volume was removed under
121
salvage operations with a very meager quantity in favour of right holders of course. The
method of calculating yield from PB I of FS II was the same as for the forests of PB I of FS I.
In FS III no yield was prescribed. All removals were reserved for meeting the demand of right
holders.
A sequence of felling of FS I was laid down for seeding and final felling in Para 94.3(a) and
94.3(b). An area of 162.25 ha was prescribed for seeding felling in PB I and 42.90 ha in final
felling of FS I; similar sequence of felling of PB I of FS II was laid down in para 94.4(a).
Subsidiary Silvi-Cultural operations such as disposal of felling debris, subsidiary felling, weeding,
cleanings, sowing and planting were prescribed. Besides, misc. regulations such as closure,
grazing, grass cutting, fire protection, control burning, fire lines, resin tapping etc. were also
included in the concluding paras of this WC.
7.32.1.1: RESULTS OF WORKING:
7.32.1.1 (i): FELLING SERIES-I:
No felling was done according to felling programme because of ban on green felling. However,
every year salvage removals were done and accordingly following table show removals as well
as deviations upto 1995-96 i.e. 14 years, in M3.
Table 46: Deviation
FS I / FS II
PB-I
PB I
(FS II)
PB-II
PB Others
(FS II) PB-III PB-IV
Prescribed yield 30000 31500 nil 32250 11200 4900
Removals
15094.89
7217.44
1923.53 6213.50 3576.78
Deviation (-)9894.47 (-) 31500 (+) 7134.25 (-) 30326.47 (-) 4986.50 (-) 1323.22
7.32.1.1 (ii): REGENERATION POSITION:
Seeding felling in PBI were not done according to the prescribed felling programme in all the
felling series. However, 693 ha area of existing blanks in PB I and other areas was planted
during the plan period. The details of areas planted year wise is given in the Annexure A.
7.32.1.1 (iii): SOWING AND PLANTING:
No planting programme was prescribed, no sowing and planting in PB I areas was done after
seeding felling as no such felling were done. However, planting on 116 ha was done in small
patches wherever open patches were available.
7.32.1.1 (iv): CULTURAL OPERATIONS:
Cultural operations such as cleanings and thinning were not carried out due to ban on green
felling.
7.32.1.1 (v): FIRE PROTECTION AND CONTROL BURNING:
Although control burning was suggested and broad rules given, no annual programme for
control burning was prescribed. The result has been that the practice was not fully adhered to.
7.32.1.1 (vi): CRITICAL APPRAISAL :
122
1. Yield on 1-4-1995 is deficit in all the PBs in felling series I except in PB II, where the excess
removals are due to salvage removals. Over all position of yield in Felling Series I is (-) 9369.35
m3; yield in FS. II and PB I was deficit, whereas it was in excess for PB Others.
2. The overall position of yield being excess removals of 1494-87m3 in FS II. No yield was
prescribed in FS III and no removal made in salvage. Because of no felling in PB I areas in FS I,
regeneration operations could not be taken up.
3. Stock maps need to be updated.
4. Demand of right holders was assessed as 800 m3 for PB II & PB IV of FS I and another 2150 m
3 for
PB others of FS II. Against this 1553.34 m3 were given to right holders showing thereby variation
of (-) 1396.66 m3. Assessment of right holders demand was on the higher side.
5. Upper limit of 35 cm, diameter of advance growth was quite high and this could have resulted in
large variation in age classes within the same periodic block.
6. There are a large number of regenerated chil areas in PB I & PB IV in the WC which require
immediate removal of over head shade. This silvicultural requirement of crop is not being
fulfilled due to ban on green felling. Thus, regeneration of Chil is suffering due to suppression.
Similarly, the mature chil trees in PB I areas are also not being felled under seeding felling, due
to ban on the felling of green trees and this will up-set the Mitchell and Walter Rotational
closure scheme (1919).
7. Yield calculations in PB I were based upon the retention of 20 trees (III/5, IIA/8, IIB/7) per ha
whereas in practice some IA trees in addition to III, IIA and IIB class trees are also retained. This
had resulted in prescribing of higher yield.
8. Rill method of resin tapping was started in 1986 in this division. Complete switch over to this
method was completed by 1991. Resin tapping by Rill method was not done as per guidelines
with the result that 50% more area per blaze was tapped in most of cases. This caused a lot of
damage to trees of lower diameter classes i.e. III class. Tapping of intervening space between
two channels (French cup and Lip method) by Rill method resulted in girdling of trees.
Therefore, tapping of lower diameter classes by Rill method has been found unsuitable.
9. In general growing stock in chil WC was not depleted on account of ban on green felling.
7.32.2: COPPICE WORKING CIRCLE:
This working circle constituted of 1512.97 ha which included RF area 961.81 ha of Jawalamukhi
, Nagrota Surian and Dehra Ranges (part) and CFS area 551.16 hectare of Jawalamukhi and
Dehra Ranges and better stocked, dry deciduous scrub forests. The object of management was
to maintain the forests in their natural form and improving their stocking through planting and
also to meet demand of right holders for fuel fodder and small timber.
Total enumeration of khair trees in 5 cm dia classes down to 10 cm dbh was done and yield was
prescribed by area but the out turn was to be shown separately. No khair tree below 15 cm
dbh was to be felled. The forests were to be managed under Coppice with Standard System
with 30 years rotation of coppice. Plantation of suitable species for supplementing the coppice
was suggested. Method of executing felling and sequence of felling were also laid down.
123
7.32.2.1: RESULTS OF WORKING:
An area of 299.37 ha has been felled under Coppice with standard system against 642.55 ha
(upto 1995-96) prescribed. The deviation is (-) 343.18 ha. Out of 299.37 ha felled upto 1995-96
the position of regeneration is as under:
Area Felled 299.37 ha
1. Area of natural 33.95 ha
regeneration (Un-
felled)
2. Area fully regenerated 76.03 ha
/planted coppice Stock
3. Area partially 73.50 ha
regenerated
4. Area poorly regenerated 69.80 ha
5. Blanks 46.72 ha
7.32.2.1 (i): CRITICAL APPRAISAL:
1. Out of 299.37 ha area felled in this WC, only 110 ha (43%) area has regenerated. The blanks and
under-stocked areas (190.02 ha) are yet to be regenerated. Felled Coppice coupes were not
vacated by the HPSFC in time in most of the cases, with the result that these could not be closed
in time. The Coppice shoots of March and April in such areas were damaged by cattle.
2. Main object of management was to maintain original character of the crop, but this has not
been achieved because of the following reasons:
i) The dry deciduous mixed scrub forests have been converted to more or less pure khair
forests as most of the felled coppice areas have been generally planted with khair only.
ii) The important species i.e. Anogiessus latifolia is almost disappearing from the felled areas
due to:
a. Technique for regenerating the species artificially has not been established.
b. The standards retained for Anogiessus species are very heavily lopped with the result
that they do not produce any seed.
c. Bush growth is dense. It does not allow seed to come in contact with the ground,
therefore, natural regeneration is also absent.
d. The coppice shoots of felled stumps are damaged /cut by right-holders for fodder.
e. The coppicing power of Anogiessus trees is also decreasing with the increase of age of
such trees.
3. The tending and other silvicultural operations were not carried out as per prescriptions
in the felled areas. The closure of areas was not effective. The coppice shoots were not
tended, singling of coppice shoots was ignored.
4. Natural regeneration was not freed from suppression.
5. No treatment for Lantana infested areas with dense bush growth was laid out by the
WPO
6. The system has completely failed in areas having tall and dense growth of Lantana or
other bushes. Therefore, the desired results were not achieved in the working circle.
There are a large number of felled areas which could not be fully regenerated although the
felling was done right in the beginning of the current working plan. Such areas require
special treatment so that these are regenerated without any more loss of time.
124
7.32.3: PLANTATION WORKING CIRCLE:
This includes blanks, young plantations and under-stocked and degraded misc. scrub areas.
Total area of W.C. is 2061.37 ha. The main object is to nurse existing plantation and to restock
the blanks and area under useless scrub species with higher utility species. These areas were
also to meet demand for fuel wood, fodder and small timber of local people.
Four plantation series were created i.e. legal closure planting Series (FSI) Voluntary Plantation
Series (FS II), CFs Plantation series (FS III) and Road and Railway side plantation series. Khair
and chil were enumerated in plantation series I & II. Stock maps for all compartments have
been prepared and placed in compartment history files. Scrub forests were to be managed
under Modified clear felling system leaving about 30-40 trees/ha as standards for seed
production and for meeting demand of right holders. No felling programme was prepared.
Control of yield by areas was prescribed.
Plantation programme was framed upto 1995-96 and 747.61 ha was prescribed for planting
with a note that DFO may exceed the annual plantation target depending upon the availability
of areas, budget allotment and administrative considerations.
Against this prescription, only 595 ha was planted (till 1996) leaving a wide gap to be covered.
Planting on Railway and Road strips was also prescribed as Lump-sum without laying any
particular sequence. Suggestions for maintenance of planted areas and cultural operations
were given.
Areas below 8 ha have shown better planting success than other areas. The larger areas like
0.10 D, Bilaspur, CFS Bilaspur, CFS Tatachan etc. have shown a lot of failures.
7.32.3.1: CRITICAL APPRAISAL:
a. The areas of plantation series IV-b could not be planted on account of non-availability of areas.
Achievements in case of FS IV are also not very clear in the absence of information. The
sequence of Planting for raod & rail side stripes, laid down in para 138 was not followed. There
has been no earmarked funding for this activity which is why it has remained neglected. Further,
avenue plantations along roads are done by the PWD. The FD also did not have appropriately
sized nursery stock of species that are recommended for such planting.
b. Closure of 10 years for plantation raised in plantation series I as suggested, is too short for B/L
species. The closure period should have been at least 15 years in order to fully regenerate the
area. More area should have been prescribed for planting during the plan period. ??
c. WPO had not prepared the list of successful plantations. There is no data available by which we
can assess as how much area under different species has been raised successfully in the past.
d. No cleaning, thinning, pruning and other cultural operation programme was laid down for
existing plantations with the result that this operation remained un-attended during the plan
period.
e. WPO had not discussed the type of areas which were/would be available for plantation in this
working circle under each plantation series. It has been noticed in the field that pure chil areas
have been planted with Khair and vice-versa. Clear guidelines are required to be laid down with
regard to the choice of species for each area.
f. No guidelines have been laid down for tackling Lantana infested areas and scrub forests with
heavy bush growth.
g. In plantation series II, it was suggested to raise three rows of fodder species all round the
plantations; this was not practicable and was not followed.
125
h. No sequence of felling was laid down for misc scrub forests with uneconomic species and their
replacement by species of more utility and economic value.
i. Although the enumeration of khair was done but no sequence for the removal of mature and
over mature trees was laid down with the result that khair trees in this WC have become over-
mature and have lost their economic value. But a ban of green felling in HP came into effect
after 1983-84 and the issue of felling khair in Govt forests still persists.
7.32.4: PROTECTION WORKING CIRCLE:
The forests with steep and difficult slopes and eroded situation were allotted to this WC. The
general character of vegetation also varies from low lying areas near Pong Dam to higher areas
of Nagrota Surian and Jawalamukhi Ranges. Area of the WC was 13,172.40 ha in Jawalmukhi, N-
surian and Dehra ranges. The object being protection, no felling except dead, dry and fallen
trees and trees for right holders, were prescribed. Total enumeration of khair down to 10 cm
dbh in 5 cm dia-classes was done. Felling on only khair trees under Selection principles was
allowed under Khair (overlapping) WC.
Table 47: Abstract of Khair enumerated under Dehra Felling Series (1980-81): Dia classes in
cm.
FS 10-15 15-20 20-25 25-30 30-35 35-40 40-45 45-50 50-55 Total
I 29769 26697 25799 11117 7767 2968 1160 90 nil 105367
II 85935 72310 19417 7098 4544 1995 900 41 4 192244
Total 115704 99007 45216 18215 12311 4963 2060 131 4 297611
In 1981 it was assessed that about 32% of the WC was made up of blanks and the average tree
density in the remaining area was about 0.3.
An area of 5504.58 ha was prescribed for planting with a sequence and technique of planting.
An area of 181.24 ha was planted out of the above said prescription upto 1995-96.
7.32.4.1: CRITICAL APPRAISAL:
As per deviation statement 9476.78 m3 has been removed upto 1995-96 (the end of the Plan)
against no prescription; This is because of salvage removals combined with right holder’s
markings (29.52 m3).
The planting programme was not followed. Tending operations were generally not carried out.
Large size areas prescribed for planting could not be seriously attended to.
7.32.5: KHAIR OVER LAPPING WORKING CIRCLE:
This WC overlapped chil and protection WCs and covers DPFs, UFs and UCs and Society Forests.
Object of this WC was to harvest mature and over mature trees of khair and also to increase the
proportion of khair in suitable localities by tending coppice shoots and natural regeneration and
planting of khair. The management system adopted was selection system with 25 cm dbh as
exploitable diameter and 15 years felling cycle. All the areas were to be gone over once in the
plan.
Enumeration of khair was done in chil and protection WCs in 5 cm diameter classes down to 10
cm dbh. No enumerations were carried out in co-operative Society Forests.
126
Table 48: Abstract of khair trees enumerated in Chil WC for Dehra Felling series in 1981 was:
Dia classes in cm.
Range Area Ha 10-15 15-20 20-25 25-30 30-
35
35-
40
40-
45
45-
50
>50 Total
Felling Series I
J’mukhi 99.54 1142 857 397 235 70 66 12 nil nil 2779
N
Surian
738.92 42410 30787 28259 12013 8325 3324 1391 206 85 126800
Total 838.46 43552 31644 28656 12248 8395 3390 1403 206 85 129579
Felling Series II
J’Mukhi 1625.79 36679 31588 6139 422 85 14 6 nil nil 74933
Dehra 638.53 27210 21467 1682 11 nil nil nil nil nil 50370
N
Surian
2526.40 26708 18500 12159 7236 4645 2012 909 47 8 72234
Total 4790.72 90597 71555 19990 7669 4730 2026 915 47 8 197537
Three felling series viz. FS I, FS II &FS III were suggested. Yield of 45000 trees by Brandies
method was prescribed in FS I and II against which 5390 trees were felled under salvage
operation, whereas in FS III yield was to be controlled by area with annual cut of 40 ha Thus
against 407.76 hectare area prescribed in felling series III, 307.34 hectare area was felled in
salvage operations.
Sequence of felling and method of executing felling were prescribed. Khair trees granted to
right holders were also to be counted toward yield. No closure was proposed in case of pure
khair areas to protect and tend the coppice shoots. No planting programme was laid down.
Felling cycle of 15 years was prescribed for all trees above 25cm, to be felled on selection basis.
For having good coppice shoots 10 cm stump height was suggested.
7.32.5.1: CRITICAL APPRAISAL:
As per deviation statement for 1995-96 removal is 5390 trees against prescribed 45000 trees in
FS I & FS II. In FS III 307.34 ha has been gone over against 407.76 ha prescribed. It appears that
felling in Govt forests came to a virtual halt after the state banned green felling in 1983-84.
7.32.6: WILDLIFE (OVERLAPPING) WORKING CIRCLE:
This working circle includes Pong Lake and nearby fringe areas. The object was to preserve,
protect and promote wildlife in and around lake areas. A brief note on the Pong WLS is below:
PONG WETLAND (RAMSAR SITE) & WILDLIFE SANCTUARY Th e pon g wet land , o f fers a winter abod e for the migratory b irds comin g from th e trans -
Himalayan zon e. Dur in g 1994, i t was d ec lared a wet land of n at ion al importan ce b y th e
MoEF. I t was accord ed intern at ion al s tatus as a “Rams ar” s i te dur ing 2002. Th e area fa l ls in
b iogeographic zon e 4-a.
CO-ORDINATES: LATITUDE 310 49’ 50” TO 32
0 14’ 35” N
LONGITUDE 750 53’ 3” TO 76
0 17’ 52” E
127
ALTITUDE UPTO 1450 FEET LEVEL AROUND THE LAKE
AREA: 307 SQ KM AS PER NOTIFICATION.
TEMPERATURE VARIES BETWEEN 4.5O
C TO 45O
C
RAINFALL: AVERAGE ANNUAL RAINFALL IS 1120 MM
L e g a l s t a t u s : i n i t i a l n o t i f i c a t i o n i n 1 9 8 3 v i d e n o . f t s . ( f ) 6 - 5 / 8 2 d a t e d 1 . 6 . 1 9 8 3 . T h e
f i n a l n o t i f i c a t i o n w a s i s s u e d i n 1 9 9 9 b y g o v t . o f H P v i d e N O . F F E - B
( F ) 6 - 8 / 9 9 d a t e d 2 3 . 1 0 . 1 9 9 9 u n d e r W L P ( A C T ) , 1 9 7 2 .
t r e e s i n c l u d e a n o g e i s s u s , l a n n e a , a c a c i a , s t e p h e g y n e , a e g l e , b o m b e x ,
s y z y g i u m , f l a c o u r t i a , z i z y p h u s , m a n g i f e r a , c a s s i a , w e n d l e n d i a ,
e m b l i c a , f i c u s s p p , d i o s p y r o s t e r m i n a l i a , a l b i z z i a e t c . s h r u b s i n c l u d e
c a r i s s a , d o d o n e a , w o o d f o r d i a , a d h a t o d a , m u r r a y a , n y c t a n t h u s ,
m a l l o t u s , e u p h o r b i a , z i z y p h u s m u m m u l a r i a , l a n t a n a e t c c l i m b e r s
b a u h i n i a , p u e r a r i a , m i m o s a , c i s s a m p e l o s , c l e m a t i s c a e s a l p i n i a , a b r u s ,
c a s c u t a c r y p t o l e p i s i c h n o c a r p u s e t c . G r a s s e s c o n s i s t o f
d e n d r o c a l a m u s , e u l a l i o p s i s e r i o p h o r u m , c y n o d o n c h r y s o p o g o n ,
h e t r o p o g o n , b o t h e r r i o c h l o a t h e m e d a c y m o p o g o n , a r i s t i d a t y p h a e t c .
T h e W L S h a s m o r e t h a n 2 0 s p e c i e s o f m a m m a l s : i n c l u d i n g l e o p a r d , s a m b a r ,
b l u e b u l l , b a r k i n g d e e r , j a c k a l , j u n g l e c a t , r u f o u s - t a i l e d h a r e , w i l d
b o a r , p o r c u p i n e , l a n g u r a n d m o n k e y s ; m o r e t h a n 2 3 0 s p e c i e s o f b i r d s
h a v e b e e n i d e n t i f i e d i n c l u d i n g t h e m i g r a t o r y b i r d s a r o u n d t h e w e t l a n d
w i t h o v e r 6 9 s p p . o f w a t e r b i r d s . T h e b a r h e a d e d g e e s e i s t h e m o s t
c o n s p i c u o u s b i r d d u e t o i t s s i z e a n d n u m b e r s ; t h e o t h e r s a r e s a r u s
c r a n e s , s t o r k s , g r e b e s , d u c k s , t e r n s , s k i m m e r s e t c . a m o n g s t t h e
p h e a s a n t s r e d j u n g l e f o w l , p e a f o w l a n d k a l i j p h e a s a n t s a r e t h e r e .
R e p t i l e s i n c l u d e s e v e r a l s p e c i e s o f l i z a r d s a n d s n a k e s . A b o u t 2 7
s p e c i e s o f f i s h e s h a v e b e e n r e p o r t e d .
HUMAN BIRD CONFLICT: THERE ARE TWO TYPES OF CONFLICTS: ONE DUE TO FISH EATING BIRDS AND OTHER DUE TO
GRAZING BIRDS. THE FISHERIES DEPT BLAMES DECREASE IN ANNUAL CATCH TO FISH EATING BIRDS LIKE CORMORANTS,
TERNS, SKIMMERS, DARTERS. GRAZING BIRDS HAVE BEEN SHOWING CONTINUOUS INCREASE IN NUMBERS DUE TO
AVAILABILITY OF GREEN FODDER / GRASS / CROPS SOWN IN THE DRAW DOWN AREA. AGRICULTURISTS USE FERTILIZER
AND INSECTICIDES WHICH ARE A THREAT TO THE FISH FAUNA AND BIRDS.
128
VILLAGES AND POPULATION: THE AREA TILL 1410 FEET HAS BEEN ACQUIRED BY BBMB AND NO PRIVATE LAND EXITS IN
IT. BETWEEN 1410/ AND1450
/ FEET THERE ARE ABOUT 64 SMALL AND BIG VILLAGES INHABITED BY MORE THAN
27,000 HUMANS AND 12,000 LIVESTOCK. BESIDES LINK ROADS AND A RAILWAY LINE LIE WITHIN THE SANCTUARY.
ABOUT 1500 FAMILIES ARE DIRECTLY DEPENDENT ON THE WETLAND FOR COMMERCIAL FISHING WHICH IS PRACTICED
FROM THE VERY INCEPTION OF RESERVOIR. ANOTHER 3500 FAMILIES ARE DEPENDENT FOR THEIR AGRICULTURE
CROPS IN THE DRAW DOWN AREA. CATTLE, C. 20000, BOTH DOMESTIC AND NOMADIC, GRAZE HERE. OVER
1,50,000 WATER BASED BIRDS ARE DEPENDENT ON THIS WETLAND DURING WINTER. THE DISTURBANCE LEVELS
WITHIN AND AROUND THIS WLS ARE VERY HIGH.
PROBLEM AND THREATS:-
I) ENCROACHMENTS: PEOPLE DO TEMPORARY ENCROACHMENTS AS THE WATER LEVEL RECEDES, BUT ABOVE MAX
LEVEL OF WATER ATTAINED ANNUALLY, PERMANENT ENCROACHMENTS ARE COMING UP. II) DENUDATION OF
CATCHMENT LEADING TO SILTATION: THE WHOLE CATCHMENT OF THE RESERVOIR, ABOUT 12000 SQ KM, NEEDS
TREATMENT. SILTATION, BESIDES SHORTENING THE LIFE OF THE RESERVOIR AFFECTS THE WATER QUALITY AND
QUANTITY WHICH ADVERSELY IMPACTS THE WETLAND. III) WEEDS: THERE IS NO PROBLEM OF AQUATIC WEEDS BUT
LAND WEEDS LIKE LANTANA, CONGRESS GRASS, CASSIA TORA ETC. NEED ERADICATION. IV): FISHING: MORE THAN 300
MT OF FISH IS EXTRACTED ANNUALLY. BIRDS GET ENTANGLED, DISTURBANCE CAUSED BY FISHING BOATS AT ALL TIMES,
TEMPORARY CAMPS OF FISHERMEN; ALL POSE A POTENTIAL THREAT TO THE BIRDS. V): GRAZING: MORE THAN
20000 CATTLE INCLUDING ABOUT 6000 OF NOMADS GRAZE THE WETLAND AREA AFTER MARCH – APRIL TILL
SEPTEMBER. BESIDES THE ILL EFFECTS OF GRAZING LIKE EROSION, DAMAGE TO THE EGGS AND HATCHLINGS OF THE
BIRDS WHICH BREED ON THE GROUND IS SIGNIFICANT. THE AFFECTED BIRDS ARE TERNS, PRATINICOLE, LAPWINGS AND
SKIMMERS. VI): POACHING: MIGRATORY BIRDS ARE EASY PREY FOR POACHERS AS THEY NUMBER IN THOUSANDS AND
ALSO RAID PRIVATE LANDS.
CONSERVATION MEASURES: BESIDES PROTECTION, HABITAT IMPROVEMENT, AUGMENTATION OF FOOD RESOURCES,
ANTI GRAZING DRIVE, UPROOTING OF WEEDS, A COMPREHENSIVE WETLAND DEVELOPMENT / MANAGEMENT PLAN
INVOLVING THE PEOPLE LIVING JUST ON THE PERIPHERY IS READY & NEEDS URGENT IMPLEMENTATION.
54: Baldev Singh 5th
Working Plan for the Forest of Una and Dehra (Part) Divisions 1981-82 to
1995-96:
7.33.1: Bamboo Working Circle:
Bamboo working Circle constitutes 723.87 hectare. This area was further divided into A and B
type = 649.77 ha & And C type = 74.10 hectare. The entire area includes Reserved forests of
two Ranges namely Dehra Range (part) 98.70 hectare and Dadasiba Range DPF= 625.17 ha
felling programme was laid down for C type only. Against 146 ha area prescribed only 7.6
hectare was felled. But no planting programme was laid down neither any survey programme
prescribed.
7.33.2: Khair Overlapping Working Circle:
This working circle is overlaps Chil shelter wood WC only and spreads over an area (over
lapping) of 4195.73 ha. Of this, Dadasiba Range included DPF=875.72 ha and UPF=2670.05 ha
whereas Dehra Range (part) included RF=81.44 ha and UCF 568.02 ha totaling 4195.73 ha. The
entire area was prescribed for felling during the plan under revision against which 1500 trees
and 2834.06 ha =13357 trees were felled under salvage operations. Felling cycle of 15 years was
prescribed and all the trees above 20 cm dbh were prescribed to be felled. No regular felling
was carried out. As a result mature khair trees remained in the forests which ultimately became
129
over mature and led to deterioration of quality. The trees/area prescribed for removal does not
match with trees/area actually felled. It appears the yield was not calculated properly. No
planting programme was laid down.
7.33.3: Coppice Working Circle:
Coppice working circle is constituted of 3457.34 ha area. The entire area was further divided
into two types, viz A type area –1449 hectare out of which 885.75 ha was prescribed to be
felled in the plan under revision against which 403.20 hectare could be felled. B type area
=2007.35 ha for which no commercial felling was prescribed. No proper felling programme was
followed due to ban on green felling. As a result felling remained in arrears. Except for Dadoa
area, no other area was felled under coppice and it could not meet the subsidiary silvicultural
requirements such as cleaning singling etc. As a result uniformity of the crop was disturbed and
mature trees remained in the forest. Openings creating in salvage operation invited weeds.
Planting for A type area was prescribed in the years following the year of felling. B type area
=771.32 hectare were also prescribed for felling but only the removal of scrub growth followed
by planting.
7.33.4: Protection Working Circle:
Total area of Protection Working Circle in plan under revision was 1233.67 ha. Felling
programme was laid down but no yield was prescribed. Planting was not thought to be
practically feasible. Soil conservation measures were suggested as warranted, depending on the
availability funds.
7.33.5: Chil Working Circle:
Chil Working Circle was constituted of an area of 4195.73 ha which included Dehra Range (part)
RFs=81.44 ha, UCF=568.52 ha and Dadasiba, DPF=875.72 ha and UPF=2670.05 ha. Felling series
viz. Legal closure and voluntary closures were suggested. No yield was prescribed for legal
closure series. Yield in voluntary closure series was prescribed in PBIV area=620.21 ha. for the
removal of overhead trees and also removal by way of thinning in the congested crop. Removal
from salvage and in favour of right holders was to count towards yield. 7700 M3 yield was
prescribed to be removed from PBIV areas against which 42776.09 M3
was removed under
Salvage felling, leading to a vast deviation of +35076.09 M3. The entire removal was under
salvage operation due to fire burnt trees. A very minor vol. given to right holders is also part of
this huge vol. removed. During W.P. field operations, it has been observed that interest of chil
regeneration was neglected and preference was given to khair and other B.L. species. As a
result chil regeneration was greatly hampered. Against 1074.51 ha only 350 ha chil area was
regenerated.
7.34: A LOOK BACK AND THE ROAD AHEAD:
The first Working Plan for Kangra by Hart commenced in 1903-04. It is over a hundred years
now since “scientific” forest management has sought to be implemented over the forests through
six WPs varying between ten and thirty years. The Century has also seen the original Kangra
forest division areas split into Dharamshala, Nurpur, Palampur, Una, Hamirpur and finally Dehra
forest divisions, the latter being set up in 1983-84. Kangra has also had part of its forests
managed through the Kangra Forest Co-operative Societies formed since 1940 and which
continued to get government support till 1973.
130
The Co-operative Forest society scheme was sanctioned by the Govt. vide letter no.568 dated
27th Feb.1940. By the end of 31-03-1953, 71 societies were complete each with an approved
working plan with a total area of 58748 Acres / 23499 ha. The scheme was further reviewed in
detail and extended for a period of ten years w.e.f 01-04-1961 with certain modifications. After
reviewing the functioning of CFS Himachal Pradesh Govt. further extended the same up to 31-
03-1973 under usual terms and conditions as laid down in Pb. Govt. Memo dated 21-11-1961
vide H.P Govt. letter No. 4-55-70-SF dated 31-03-1973.
Assessment of Various WPs:
Hart’s WP (1903-04 TO 1921-22) had satisfactory results. Though many of its prescriptions
could not be fully carried out, the Chil forests improved. Conditions, however, necessitated early
revision of this WP and this resulted in Walter’s Revised WP (1920-21 to 1929-30). This WP
apparently ‘misfired’ in that due to application of the Uniform System across the board, yield
prescriptions were far higher than warranted by the condition of the forests with varying
topography and related factors. Reportedly a “huge conflagration” broke out in 1921 and many
of the trees which were to count towards annual increment were wiped out.
Mohan’s Revised WP was for 20 years, 1930-31 to 1950-51. The prescriptions and suggestions
of various Working Circles were almost fully implemented. Shelter wood System introduced by
Walter in 1921 and continued in this plan for Chil and Oak, proved suitable. In all working
Circles natural regeneration was adequate and fairly good, artificial regeneration was also
obtained. The demands of right holders were fully met with. Felling except in Chil Shelter wood
Working Circle, were only slightly behind the schedule and proved beneficial to the crop. A
large number of buildings, roads and bridle paths were constructed. Deodar was artificially
introduced though on a limited scale, in comptt 3 of D.P. Dharmkot, DP Chakbar, Kareri C 5, P.
42. K Leondnal C 1. It has done very well in case of D.P. Dharmkot and Chakban Kareri while in
Leondnal it has failed.
The next Revised WP by Romesh was for 30 years, 1951-52 to 1980-81. In the first half of this
WP there was excess felling over the prescribed yield and regeneration also did not keep pace.
Between 1962 & 1965 Eucalyptus was introduced in clear felled areas, but as it did not live up
to its promise, Eucalyptus plantation was done away with in 1966-67. But strangely quite large
scale Eucalyptus plantations continued to be carried out till the mid 1980s especially in forest
divisions of Kangra Circle. Conditions, however, necessitated early revision of this WP.
Malhotra’s WP, 1966-67 to 1980-81, had 8 Working Circles in it. Apparently, the Chil Shelter
Wood WC did well in places where fires were controlled and closures were respected.
Problems with adequate natural regeneration, however, continued to persist. There were
unexplained excessive removals in various PB including PB I. Forest Working was nationalised in
1975 and much of the damage to chil trees has been attributed to faulty resin tapping since
then. Plantation activities especially of Chil and Khair have picked up since the 1980s and have
not looked back. This has been mainly due to the 20 Point Programme which is Centrally
monitored till today and has plantations as one of the monitor-able points with annual targets
allocated by GoI.
131
The first Integrated Working Plan for the Cooperative Societies of Kangra district was compiled
by Rawal for the period 1967-68 to 1982-83. There were 29 Cooperative Forest Societies in
Dharamshala and Dehra (Part) Forest Division. It appears that the prescriptions for Chil, Coppice
and Plantation WCs under this WP worked well and did good to the forests. More than 50 % of
the felled areas were naturally regenerated and plantations did well too. The relatively better
performance of the KFCSs could be attributed to broader and keener public participation than
elsewhere. KFCSs were, however, found to be weak in book / record keeping.
7.35:M.P.SINGH PLAN, (1981-82 TO 1995-96): This is probably the most well articulated and
coherent WP written for the tract which includes the present day Dharamshala and Dehra
forest divisions. During this period there were two epochal changes that continue to influence
the course and content of forest management, hopefully for the better. The year 1980 saw the
enactment of the FCA, 1980; a concurrent legislation that only allowed diversion of forest land
for non forestry purposes after approval of the MoEF. Second, in 1983-84, the GoHP banned
green felling in forests of the state and this was later endorsed by the Supreme Court of India in
1996. Both these developments have been instrumental in putting an end to wanton diversion
of forest land for other purposes including distribution of forest land to the landless / marginal
farmers. The green felling ban stopped in its tracks the often grandiose felling plans / series that
still dominate the forest management discourse as articulated in WPs.
Most of the felling prescribed in this WP could, therefore, not be carried out and this actually
benefitted many of the forests. The case that seeding felling alone results in natural
regeneration no longer held true as ground conditions towards the close of the century had
completely changed. Human and other biotic and development pressures continue to squeeze
the forest estate.
CHIL SHELTER WOOD WORKING CIRCLE
Due to ban on green felling, the Chil stock was not depleted; however, excess removals in PB
Others are recorded and attributed mainly to salvage removals caused due to faulty tapping for
resin even after introduction of the rill method. This method has been found particularly
damaging to the smaller girth chil trees.
COPPICE WORKING CIRCLE
Even though less than half of the prescribed area under this WC was felled, regeneration
remained a problem. Plantations taken up in the cleared areas were almost purely of khair and
the original, native BL species were neglected. Natural regeneration was deficient due to
emergence of lantana and other weeds. It would seem that due to emergence of new inhibiting
conditions like the spread of lantana and more intense fires occurring now, the earlier
assumptions on which these silvicultural principles rested were being set aside and fresh
management approaches were required.
PLANTATION WORKING CIRCLE
It is noticed that the plantation area actually planted against the target prescribed fell short.
What is worrisome is that we do not know about the fate the plantations that were taken up
under this WC. This is because no records in terms of proper plantation journals have been
maintained and the few that might have been maintained are either destroyed or lost. There
are no entries about plantations, their success or otherwise in CH files and so after 15 years of
implementation of this WC, there is virtually no record of the plantations done or their fate.
132
Casual observations, however, indicate that the obvious large scale failures of plantations
(except perhaps those of chil and khair) can be attributed to a host of factors that continue to
be ignored / not addressed till today. The role of fires in destroying new plantations, especially
in scrub and chil tracts, has not been properly recorded, analysed and therefore not understood
to enable formulation of effective strategies to counter the large scale mortality in plantations.
Similarly, tackling grazing, effective closure, quality of plants raised in nurseries and so forth
continue to plague even valiant efforts to artificially regenerate forests. This is apparent from
the absence of any data, discussion or analysis on these counts in current or past Working
Plans.
PROTECTION WORKING CIRCLE
This is one of the more weird WCs, not conceptually, but in terms of management
prescriptions, actual working and therefore a reflection of the “timber” fixation of foresters. A
huge area of over 13, 000 ha has been assigned to this WC. These are described as steep and
precipitous forests and their average density assessed at 0.3. Clearly most of them are heavily
infested with lantana and other obnoxious weeds. The forests have many blanks, BUT
apparently have khair trees scattered across them. This apparently is the temptation and so
total enumeration over this huge area was got done and all khair trees down of 10 cm dhb were
measured and numbered. Why one would ask especially when no yield by number of trees or
area has been prescribed? And what happens?
9947 m3 of “salvage” timber is removed from this WC during the Plan period. One the other
hand against the 5505 ha of area prescribed for planting under this WC only 181 is carried out!
(ofcourse what happened to these 181 ha is also not known). The saving grace about WP
prescriptions is that by the time it is discovered (if ever) about how they have been flouted
there are neither records nor the persons concerned to provide any answers!
KHAIR OVERLAPPING WORKING CIRCLE:
In this case, 45,000 khair trees of over 25 cm dbh were prescribed to be felled, but only about
5000 odd were actually felled. The green felling ban apparently came in the way. However, of
the 407 ha of area prescribed to be gone over for felling khair, over 307 was gone over via the
route of salvage felling. It would seem that over 75% of the prescribed area fell victim to forest
fires or have salvage removals become a front to side step the ban on green felling? Either way
the forests continue to suffer. They have many over mature trees of khair when not felled or
have nearly everything cleared when marked for salvage removals, inviting large scale invasion
by alien species.
7.35.1: Baldev Singh 5th
WP for the Forest of Una and Dehra (Part) Divisions 1981-82 to 1995-
96:
It appears that due to the ban on green felling, there have been less removals than prescribed
in Coppice, Khair, Plantation WCs. In chil WC, however, there have been massive excess
removals (+ 35,077 M3) .
133
CHAPTER VIII
STATISTICS OF GROWTH AND YIELD
8: General
The site quality of chil is corresponding to FRI site quality to III. The figures of local volume
tables for chil & other mixed Broadleaved trees as adopted by M.P. Singh for the right bank of river
Beas i.e. Jawalamukhi Range, Nagrota Surian range, Dehra Range part (Present Dehra block and
Bankhandi Block) will continue to be applicable for the tract dealt with falling on the right bank of the
river Beas.
Table 49: Volume table for the right bank
Local Volume-table: (Stem-timber and stem-small-wood)
Dia.cm Class Volume m3
10-20 V 0.05
20-30 IV 0.23
30-40 III 0.65
40-50 IIA 1.36
50-60 IIB 2.35
60-70 IA 3.62
70-80 IB 5.20
80-90 IC 5.20
90 & above ID 5.20
8.1: The above table shall be applicable for all practical purposes. However, in some special cases,
volume-table for different height-class may be required. The volume-table s compiled by F.R.I. for
various height-classes is, therefore reproduced hereunder for ready reference:
Table 50: The volume table for various height-classes
8.2: Volume table for the Left Bank
Volume table for chil adopted by Baldev Singh to the forests situated on the left bank of river
Beas applicable for Dada siba range and Dehra range part (present Pirsului & Sadwan block) of the area
99
Dia in cm Class Volume (m3) (Stem timber & Stem-small-wood Height Class)
34.75 m to
42.06 m
27.74 m to
34.75 m 21.95 to 27.74 m
10-20 V 0.098 0.098 0.098
20-30, IV 0.420 0.392 0.336
30—40 III 1.042 0.888 0.804
40-50 IIA 1.951 1.738 1.598
50-60 IIB 3.255 2.986 2.730
60-70 IA 5.209 4.629 4.020
70—80 IB 7.362 6.230 5.238
80—90 IC 7.362 6.230 5.238
90 & above ID 7.362 6.230 5.238
134
dealt with will continue to be adopted for the same areas for future also. The site quality of chil being
III/IV same is reproduced below.
Table- 51 Vol. table for Left Bank
Dia (cm) Class Volume (m)3
10-20 V 0.028
20-30 IV 0.19
30-40 III 0.65
40-50 IIA 1.44
50-60 IIB 2.60
60-70 & above IA 3.54
8.3: Diameter-Age Relationship:
The diameter-age relationship as given in the plan under revision has been checked in the field by
analyzing a sufficient number of fresh stumps. The diameter growth-rate of chil for the divisions as given
below compares reasonably well with the F.R.I. figures, keeping in view the fact that the stocking of the
new crop (P.B.IV, P.B.III and the plantation areas) is generally full.
Table 52: Diameter-Age Relationship
8.4. Volume Increment
Volume increment as worked out by M.P. Singh in the plan under revision will be adopted as
such as reproduced below for the Right Bank Felling Series I & II and CFS Felling Series III.
8.4. Volume Increment table for Right Bank Felling Series Table 53(A)
Diameter class (cm) vol. increment%
10-20 6.51
20-30 3.87
30-40 3.22
40-50 1.80
50-60 1.23
60-70 0.56
Diameter
over-bark cm 10 15 20 25 30 35 40 45 50 55 60 65
Age (Year) 30 42 52 62 72 80 92 102 104 120 135 160
135
100
Volume increment as worked out by applying Pressler`s formula in the Nurpur Forest Division and
applicable to the Left Bank in the plan under revision will continue to be adopted as such and is
reproduce below:
8.4.1 Volume Increment table for Left Bank Felling Series
Table 53(B)
Diameter class (cm) vol. increment%
10-20 --
20-30 6.84
30-40 3.98
40-50 1.64
50-60 0.41
60-70 0.41
8.5: Vol. Table for Mixed B.L. Species
The various B.L. species occur sporadically and are mainly utilized as fuel wood. The current
volume factor in use have been checked out in the field & found to be reasonably correct. The same
volume factors are therefore adopted.
Table 54: Vol. Table for Mixed B.L. Species
Dia- (cm) Class Volume (m3)
10-20 V 0.028
20-30 IV 0.141
30-40 III 0.566
40-50 IA 1.132
50-60 IIB 1.132
60-70 IA 1.415
70-80 IB 1.415
80-90 IC 1.415
90 & above ID 1.415
8.6: Fuel Wood
Fuel wood is also an important forest produce of the area. The no. of trees of different species &
diameter classes available per hectare of area under mix. B.L. Scrub species as adopted by Baldev Singh
will continue to be adopted for volume factor also for left bank of river Beas as mentioned below :-
136
101
Table - 55
Stocking per Hectare classification
Name of species Classification
V IV III IIA VB
Annogeisus latifolia 6 4 - - -
Lannea coromandelltica 1 9 4 2 -
(kembal)
Eugenia jambolana 2 3 1 - -
Eugenia jambolana var.
Albizzia odoratinima(Karmaru) 2 1 - - -
Flacourtia indica (kangu) 12 6 2 - -
Mallotus Philipinnsis 13 12 2 - -
Total 36 39 9 2 -
The stacked volume of fuel wood per hectare is estimated as 25m3
with & weight of 175 quintal
(wet). For the right bank of river Beas the fuel wood out turn as worked out by M.P. Singh will be
adopted in future also. The average out tern comes to about 475 quintal/hectare. Though this figure
should not be taken as a strict yard stick yet it will serve as a guideline in arriving at rough estimates of
fuel wood out turn from the forests dealt was under the entire tact of this plan.
8.7: KHAIR:
Khair is the most important species of the tract after chil and is used in the manufacture of katha. The
khair trees are grown from seed as also through coppicing. Plantations from seed origin up to about 10
years of age are easily distinguishable. The average result of measurements from different plantations
for 10 years done on 10 plants of each year are as below:
Table 56:
The measurements taken on 10 khair tress of coppice origin for each year are as under:
Table 57:
Age Yrs d.b.h.(cm) height (m) Age Yrs d.b.h.(cm) height (m)
1. --- 0.42 6. 3.95 4.20
2. --- 0.94 7. 5.60 5.82
3. 0.70 1.48 8. 7.45 6.30
4. 1.20 2.57 9. 7.80 7.35
5. 2.50 3.40 10. 8.00 8.85
Age Yrs d.b.h.(cm) height (m) Age Yrs d.b.h.(cm) height (m)
1 2.40 2.30 8 9.00 8.00
2 4.20 3.50 9 10.20 8.50
3 4.70 4.50 10 11.40 9.50
4 5.70 6.00 11 13.00 10.20
5 6.45 6.50 15 14.30 11.00
6 7.10 6.85 20 17.10 11.50
7 8.30 7.40 24 18.75 13.00
137
102
The analysis of the data shows that the rate of growth of the seedling crop is markedly different from
that of the coppice crop.
In view of heterogeneous nature of the crop, the data adopted from Haldwani Forest Division by
M.P.Singh and Baldev Singh for the calculation of standing volume of Khair per ha (m3) has been utilized
as under:
Table 58:
Crop
age(yrs)
Average
d.b.h. (cm)
Avg ht
(m)
No. of
trees / ha
Standing volume (stem
timber) per ha (m3)
5 (3.50) (3.50) --- ---
10 (7.60) (6.00) --- ---
15 (11.10) (8.50) (583) ---
20 (13.90) (10.90) (514) 5.59
25 16.50 (13.10) (445) 11.61
30 18.80 14.90 385 20.64
35 20.80 16.70 331 26.93
40 22.60 18.30 287 32.53
45 24.10 19.50 252 37.78
50 25.40 20.70 227 41.93
55 26.60 21.60 203 ---
60 27.70 22.50 188 ---
(The figures in bracket are extrapolated)
The table below shows the average period taken by different diameter classes to enter into the next
higher diameter class. This is derived from the above table:
Table 59:
Dia- Class
(cm)
Total age on entering the class (Yrs)
25 47 Yrs
14 Yrs
11 Yrs
8 Yrs
20-25 33 Yrs
15-20 22 Yrs
10-15 14 Yrs
138
103
8.8: It is estimated that the annual mortality rate in passing from one diameter class to the other is
about 2%; the figure for Haidwani Working Plan being 1.87%
Following table gives the diameter; total volume, heartwood volume, weight of heartwood and weight
of air dry Katha, as compiled by study of 10 trees of each diameter class:
Table 60: Total volume, heartwood volume, weight of heartwood
8.9: SOME CONVERSION FACTORS:
Data for solid volume; stacked volume and weight of fuel wood for misc. BL species was collected from
Dharamshala Fuel Wood sale depot in various seasons. The solid volume of the billets was calculated by
the quarter girth formula. The results obtained are as under:
(i) Solid volume/stacked volume = 1:2
(ii) Air-dry weight/m3 stacked volume 3.60 qtls.
(iii) Air-dry weight/m3 solid volume 7.20 qtls.
8.9.1. Charcoal
Charcoal is made mainly from chil. It is estimated that 1.05 quintal of charcoal is extracted from one
cubic mater of standing volume.
8.10: QUALITY CLASSES:
The site quality classes in respect of chil have been assessed by taking height and diameter
measurements of at least ten dominant trees in each compartment/sub compartment and by comparing
the same with the standard site quality classes given in the multiple yield tables. These have been
recorded in the respective compartment history files. The average site quality of chil is III.
8.11:DENSITY:
The canopy density of all the compartment/sub compartments has been assessed occularly and
recorded in the respective compartment history files.
8.12. Stocks Maps
Stock maps on 1:15000 scale have been prepared for each compartment, the tracings of which
have been placed in each compartment history file. Four sets of divisional stock maps have been
prepared on 1”=1 mile scale. One each for Addl Principal Chief conservator of forest working plan
Mandi, Conservator of forests Dharamsala(Now Hamirpur)circle, & Divisional Forest Officer Dehra Forest
Division Dehra.
Dia-class
(cm) Ht (m)
Standing
vol (m3)
Heartwood vol
(m3)
Wt of heartwood
(kg)
Weight air dry
katha (kg)
10-15 8.30 0.026 0.012 11.00 ---
15-20 10.10 0.069. 0.030 31.50 2.50
20-25 11.75 0.117 0.056 50.50 4.95
25-30 12.85 0.168 0.108 78.50 8.00
30-35 13.30 0.253 0.176 128.00 13.80
35-40 13.30 0.330 0.241 167.50 18.00
40-45 13.30 0.434 0.302 197.00 22.80
45-50 13.30 0.545 0.388 280.00 28.70
139
104
8.13: ENUMERATIONS:
Tota1 enumeration down to 10 cm d.b.h. in 10 cm dia-classes have been carried out for the entire Chil
Working Circle, of Khair in 5 cm diameter classes down to 10 cm d.b.h. in Chil Working Circle (felling
series I & II), Protection Working Circle (felling series I & II), Coppice Working Circle, Plantation Working
Circle (felling series I & II), and Bamboo Working Circle. The details for each compartment/sub
compartment have been given in Volume 11,appendix11
8.14: REGENERATION SURVEY:
Regeneration assessment survey of all P.B.I. areas of the Chil Shelter wood Working Circle (Felling Series
I, Felling Series II and Felling Series III), of the Plan under revision; was done and regeneration survey
maps prepared on 16” =1 miles (1: 3960) scale along with regeneration assessment report and have
been placed in the compartment history files. The definitions of completely regenerated; moderately
regenerated and poorly regenerated areas have been taken as under:
8.14.1. Sal
The site quality of sal is below quality B of FRI yield table as checked from the curve drawn by
plotting age determined from year of felling and the average height of shoots measured in different
forests in Baldev Singh`s W.P. under revision. No fresh data was possible to be collected owing to the
ban on regular felling in the tract dealt with. Therefore, data reproduced below as adopted by Baldev
Singh will continue to be adopted for all purposes.
60(A) Growth statistics of Sal
Age Girth of brest height (cm) Height No. of shoots
measured Maximum Average Minimum
3 10 9 6 4.50 25
5 15 12 7 5.80 13
6 16 14 7 5.20 12
9 17 16 8 2.30 12
10 18 17 8 7.30 14
15 21 18 8 8.20 17
17 23 18.5 8 8.50 16
22 25 19 8.5 10.40 15
24 25 19 9.5 13.50 20
30 25 20 10 15.00 15
From the above the curve drawn indicates that the sal coppice shoots grow very well for first five years,
then the diameter increment declines steeply at the age of 10 years. The behavior of sal coppice can be
explained by the fact that want of cleaning of stool shoot after five years of felling retards growth.
105
(i) FULLY REGENERATED Poles with density 75% and above.
(ii) MODERATELY REGENERATED Poles with density 50 to 75% or saplings and seedlings with density
75% and above.
(iii)POORLY REGENERATED Poles with density less than 50% or saplings /seedlings and recruits
with density 50% to 75%.
140
CHAPTER - IX
9: ESTIMATE OF CAPITAL VALUE OF FORESTS:
A rough estimate of the capital value of the forests based on the value of land and growing stock
is as under:
9.1: Land:
Total forest land Cost of land Total value
(ha) per ha (Rs) (Rs)
30108.80 10,00,000 30,10,80,00,000
9.2: Growing Stock:
Species Vol(m3) Rate(per m3)/per Total value of
meter girth growing stock (Rs)
Chil 417000 2070/- 863047315/-
Khair 510800 1330/-(per meter 679351285/-
Girth)
Misc. BL/
Fuel wood 12500 80/- 1000000/-
Bamboo 53400 15/- 800000/-
Total 993700 M3 Rs 1544198600/-