Effect of Ambient Temperature and Humidity on Plasma Cortisol in Sheep

Effect of Ambient Temperature and Humidity on Plasma Cortisol in Sheep

Br. vel.). (1982). 138, 175 EFFECT OF AMBIENT TEMPERATURE AND HUMIDITY ON PLASMA CORTISOL IN SHEEP BY V. H . GUERRI N I* AN D H . B ERTC HI NG ER...

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Br. vel.). (1982). 138, 175

EFFECT OF AMBIENT TEMPERATURE AND HUMIDITY ON PLASMA CORTISOL IN SHEEP

BY

V. H .

GUERRI N I* AN D

H . B ERTC HI NG ER

Department of Physiology, Pharmacology and Toxicology, Faculty of Veterinary Science, OnderslejJoort OJ 10, Rejmblic of South Africa

SU M MA RY

Pl as ma co rti so l, water inta ke, urin e o utput a nd th e packed ce ll vo lum e (PC V ) were d e termin ed in six adult M erin o we th e rs ex posed to ho t-humid , ho t-dry, cool-humid a nd coo l-dry environm en ts . Th e te mpera ture-humidity ind ex (THI ) was used to d e termin e th e co mbin ed effect of a mbi en t tempera ture a nd humidi ty on th e va lu es meas ured . T he lowes t m ea n p las m a co rti sol va lu es ( 19·03 ± 6· 23 nm ol/ 1) we re fou nd durin g ex pos ure to th e hot- humid environm ent a nd the hig hes t (43·64 ± 9·86 nm ol/ 1) during expos ure to th e cool-humid environm e nt. During exposure to th e ho t-dry a nd cool-dry environm ents, m ea n pl as m a co rti so l leve ls ra nged bet wee n 32·53 nm ol/ 1 a nd 4 1·56 nm ol/ 1. In creased THI va lu es were co rrelated with d ecreased pl as m a co rti so l (P <0·005) . Sh ee p whi ch h ad hig h pl as m a corti so l levels (3 2·2 1 to 58·6 1 nm ol/ 1) co nsum ed less wate r a nd ha d a lower urin e o u tpu t but a hig her PC V va lue th a n s hee p whi ch had low pl as ma co rti so l leve ls (8· 13 to 32· 13 n mol/1). In a ll th e shee p in creased pl as ma co rti so l was co rrela ted wi th d ec reased water in ta ke (P < 0·005), decreased urin e outpu t (P < 0·005) , bu t in c reased PC V (P
I NTRO D UCT I ON

E xperim e n ts ca r ried out in s heep by Ro binson & M orri s ( 1960), a nd late r by ';:'i lton , W eig l & Bu cha na n ( I 975) showed th a t d ur ing the first d ays of ex pos ure to a ho t environm e nt , pl as ma co rti so l in creased . If ex pos ure to th e hot enviro nm en t was p rolo nged p las ma co rti so l d ecreased. M o re rece ntl y, Ing ra ha m , Sta nl ey & W agner • Prese nt add ress: I.e M ils d ' /\ la ux, l.ot isscmcm Cadi lh ac, /\v . Vill ene uve d ' /\ngo ul cmc, M o n tpc lli c r 3•f I 00, Fra nee.

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( 1979) found simil a r res u lts in cattle w hi ch h a d b ee n exposed to a h o t e nv iro nm en t. In s h eep , th e initi a l in crease in co rti co id s o n ex p os ure to a h o t enviro nm e n t m ay occur as a respo n se to s tress, wh e reas th e d ec rease in pl as m a co rti sol durin g pro lo n ged h ea t expos ure m ay b e rel a ted to a d a p tat io n to st ress ful co nditi o n s (Til to n et al., 19 75). Beca use pl as m a co rti sol va lu es a r e m o difi ed b y s tress, clim a ti c eva lu a ti o ns mu st includ e th e str ess indu ced by hi g h a mbi ent humidi ty during ex pos ure to a h o t o r a coo l en v iro nm ent ( K elly & Bo nd , 197 1) . I t is fo r thi s reaso n th a t th e te mpe r a tu re- humi d ity ind ex (THI ) whi c h co mbin es th e e ffect o f a mbi en t te mpe ra ture a nd humidity o n a nim a ls w as fo rmul a ted ( I ng ra h a m et al., 19 79) . U nfo rtun a te ly, th e e ffect o f ex pos ure to a humid enviro nm e nt as co mp a red to a dr y en v iro nm e nt o n th e pl as m a co rti so l va lu es o f rumin a nts h as ra re ly bee n d escrib ed. Th ese findin gs U"11d e rlin e th e n eed to d e termin e p las m a co rtiso l in s h ee p ex p osed to diffe re nt e nviro nm e n ta l te mpe r a tures a nd humidi ty. Expe rim ents ca rri ed o ut b y Ba lfo ur ( 1962), with ca ttl e, a nd b y f a n a nd hi s co ll a b ora tors ( 19 7 5), with s h ee p , s ho wed th a t co rti coid s exe rted s ig nifi ca nt soci i u Illre ta ining ac tivi ty . O 'Co nn o r & V e rn ey ( 194·2) m a inta in ed th at th e prin c ipa l p las m a g lu coco rti co id s acco unted fo r 30 to 4 0% o f t h e sod ium-re ta inin g ac ti vit y in m a n . On th e o th er h a nd , exp erim ents h ave s ho wn th a t sod ium losses in c rease wh e n s h ee p a re ex posed to h o t enviro nm e nts (Co llin s & \ 1Ve in e r, 1968 ). R ece ntl y, Gu e rrini , K os te r & Bertchinge r ( 1980 ) d e m o nstra ted th a t th e urin e vo lum e o f s h ee p in cr eased durin g expos ure to a h o t-humid , a h ot-dry, a nd eve n a coo l- humid e nv iro nm e nt. In th e sa m e ex perim e nt, w a ter inta ke in c reased durin g b o th h o t e n v iro nm e nts but d ecreased o n ex p os ure to th e coo l-humid enviro nm e n t. Beca use bo th e n v iro nm e n ta l a nd co rti so l level ch a n ges m ay a ffec t bod y w a ter b a la n ce (Co ll in s & \A/e in e r, 1968; F a n el al. , 1975), th e re is a n eed to es ta blis h th e rel a ti o n s hip b e tw ee n pl as m a co rti so l co n ce n tra ti o n , urin e o utput a nd wa ter int a ke in s h ee p durin g expos ure to diffe re nt en v iro nm ents. L ee, R o u sse l & B ea t ty ( 1976) s h o wed th at hig h b lood co rti so l va lu es in c reased t h e pro du c ti o n o f red bl ood ce ll s in ca tt le. I n rece nt rev iew s, G u y to n ( 197 1) a nd H a rp e r , R o dw e ll & M ayes ( 1977) fo und th a t th e re was a p os itiv e co rre lat io n be tw ee n pl as m a co rti so l a nd PCV . Ex p e rim ents ca rri ed o ut in s h eep (G u e rrini et al. , 1980 ) s h ow ed th a t h o t- humid expos ure d ecreased PCV ; in co ntras t, ex p os ure to a h o t-dry e nv iro nm e nt in cr eased PCV . Beca use co rti so l m ay indu ce red ce ll produ ct io n , a nd e n v iro nm e n ta l c h a nges th e m se lves m ay a ffect PC V , th e re is a n eed to s tud y th e re la ti o ns hip b e twee n PCV a nd pl as m a co rt iso l in s h eep ex posed to diffe r ent e nv iro nm e nt s. The purpose o f th e prese nt ex p e r im e n t was to d esc rib e th e e ffect o f te m pe ra ture and humidi ty o n p las m a co rtiso l in s h ee p. A t th e sa m e tim e, th e e ffect of p las m a co rti so l c h a nges o n w a te r int a ke, urin e o utput a n d PCV we re in ves ti gated .

M ATERI A LS AND M ET HO DS

S ix a dult L ete ll e w e th e rs we ig hing betw ee n 48 a n d 52 kg we re use d fo r th e ex p e rim e n t. Th e s h ee p we r e ke pt in a n e n closed c h a m be r a nd ex posed to three tes t e n v iro nm e nts, eac h las tin g fo ur w ee ks: h o t- humid w ith hig h a m b ie nt te m pe ra tures (29 to 32°C) a nd humidity (89 to 9 7%), h o t- d ry wi th hi g h a mbi e n t te mp e ra tures (29 to 32°C) but lo w humidit y (4 9 to 53%), a nd coo l- humid w ith low a mbi en t te m pera t u res ( 18 to I9°C)

ENVIRO N1v1 ENT AND PLASMA CORT ISOL IN S H EE P

177

but high humidity (92 to 96%). Studies were a lso und erta ken ove r fo ur 'control' period s in a coo l-d ry e nviro nm ent each of three wee ks duration, befo re , betw ee n a nd a fte r th e three tes t pe ri od s. In th ese co ntrol period s th e a mbi ent tem perat ure range was 19 to 23°C a nd a mbi ent humidity range 54 to 6 1% . Milled lu ce rn e grass a nd wate r were suppli ed each d ay be tw ee n 0800 a nd 08 30 h . Each d a y, wa ter inta ke and urin e output were m eas ured at 0800 h. Ambi ent tem p eratures a nd humidity were reco rd ed co ntinu ous ly on a tam bo ur h ygrograp h (C ase ll a, London ) whi ch w as reg ul a rly ca librated to a ± 4% error m a rg in ; th e recordings a t 0800 h each d ay were used fo r stat isti ca l a na lys is . T he te mpe rat ure a nd humidi ty we re not a ll owed to va ry by m ore than ± 4% durin g a ny 24- h period . Blood samples were co ll ec ted fro m th e jugu la r vein eve ry seventh d ay be tw ee n 0800 a nd 0830 h. T he pac ked ce ll vo lum e was determ in ed b y the mi croca pill a ry me thod. Dupli ca te p las m a co rti so l concentrations were th en d etermin ed b y radioimmunoassay (Ba um , Ind o r & La nd o n, 1974·). M ea ns , sta nd a rd d evi a tion s a nd stand a rd e rro rs were ca lcul a ted a nd lin ea r regress ion a na lyses were used to test th e co-va ri a nce be tween th e va lu es m eas ured . Th e THI values were d e termin ed using th e equ a tion: THI = ( Tc~ b )- (0· 55- 0·55RH) (T ell>- 58) wh ere T ell> was the dry bu lb te mp erat ure, a nd RH was amb ient rela tive humidity ex pressed as a pa rt of I (Kell y & Bo nd , 197 1) .

RESUL.TS

Of th e six sheep studi ed , three co nsiste ntly had lower m ea n pl as m a co rti so l co nce ntra ti ons (8· 13 to 32·13 nmo l/ 1) th a n th e o th er three (32·2 1 to 58·6 1 nm o l/ 1) wh en exposed to the different environm ental conditions. Fo r thi s reaso n in prese ntin g the res ults in Fi g . I a nd Tab le 1 f th e shee p were divided into ' low' an d ' hi g h' g ro ups res pe ctively. T a bl e I shows the li nea r co rrel a tion s betwee n a ll th e va ri a b les m eas ured , i.e. hae m atoc rit, pl as m a co rti so l co nce ntrat io n , urin e output a nd wa ter intak e , w hen the s hee p were ex posed to d iffe rent enviro nm enta l co nditio ns.

TABLE I

SIMPL E CO RR ELATIO NS OF PL.ASiv! A CO RTI SO L \VITH THE TE MP ERATURE H U MIDITY I N DE X JTI-II J, WATER I NTAK E, UR I NE OU TP UT AND PAC KED C ELL VOLUME ( PCV) I N SI X SHEEP EXPOSED T O HOT -H UM ID , I-l OT-DRY AND COO L- H U MID ENV IR ON ME NTS

environments

Hal-f humid

Hot-f dl)'

Cool-f humid

-0·38 -0·30 -0·39 0·53

-0·40 -038 0·40

- 0·7 1 -05 1 0· 38

- 0·30 -0. 40 0·55

il ll*

THI unit s

VVa ter intake 1/ day U rin e outputl / day PC V %

* 144 pa irs tes ted .

t

24 pa irs tes ted .

TABLE II !'vi EJ\N ±SO WATER INTAKE, UR I NE OUTPUT, BODY WE I GH T AN D PA C KED CE LL VOL UME I N SIX MER I NO WETHERS OF WH I C H T H REE HAD CONS I STENTLY 'H I GH' AND T H REE ' LO W ' PLASMA CO RT I SO L LEVELS D UR I NG EXPOSURE TO HOT-HUMID, HOT-DRY , COO L-HUMID AND COO L -DRY ENV I RONMENTS

Hot-humid High

Low

High

Cool-dry

Cool-humid

Hot-dry Low

H igh

Low

High

26·2 1 ± 9·53 3·40 ± 0·55 2·02 ± 0·73 36·58 ± 2·8 1

42·03 ± 19·52 3·29 ± 0·36 0·89 ± 0·38 38·62 ± 4·06

Low 2

Pl as ma co rt iso l n mo l/ I * vV ate r int a ke !/ da y Urin e out put !/ d ay

PVC%* Bod y weight kg *

t t

27·91 ± 17·2 1 3·34· ± 1·04· 1· 17 ± 0·82 35·08 ± 3·23 53·20 ± 2·20

10·3 1 ± 4·23 4·47 ± 1· 10 1· 18 ± 1·01 3 1·50 ± 2·93

60·74 ± 20·3 1 4·63 ± 0·77 0·93 ± 0·43 36·50 ± 3·65 54·70 ± 1·40

19· 12 ± 9·43 5· 78 ± 0·69 1· 91 ± 0·2 1 33·50 ± 2·87

59· 58 ± 22·76 2·64 ± 0·9 1 1·37 ± 0·35 38·60 ± 3·22 56·00 ± 1·80

21·52 ± 13·86 3·99 ± 0·49 1·32 ± 0· 16 35·54 ± 2·52 53·60 ± 1·30

* 24 measurements made during exposure to hot-humid , ho t-dry and cool- humid environm ents and 72 durin g coo l-dry exposu re. 168 m eas ure ments m ad e d urin g hot- hum id , hot-dry and cool-humid exposure a nd 504 du rin g cool-dry exposure.

t

> :::0 -<

'-

0

c

:::0

2

_> r

ENVIRONMENT AND PLASMA CORT ISOL IN SHEEP

179

45 ~

0

> 35

u

CL

25

w

-"" 0

c w 0

~

w c

...... 0

E

c 0

"'

Fig . I . M ea n urin e o utput , wa te r int a ke and PCV in M erin o sheep with high (n = 3) . an d low (n = 3) 0 plas m a cort iso l leve ls. The a nim a ls were exposed to ho t-humid (A), hot-dry ( B) a nd cool-humid (C) tes t en viro nm e nt s a nd a coo l-dry (D ) co mro l environment. Th e upper bar lin e represc m s ha lf o f th e s tanda rd deviation. Durin g each tes t env iro nment , 24 blood sa mples a nd 168 wa ter in take a nd urine output m eas urement s were ta ke n. Durin g com rol enviro nm e nt s, 72 bl ood sa mples a nd 501 wate r int a ke a nd urin e ou tput measu rcmem s were ta ken.

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BRITISH VETER INARY .J OU RNAL , 138 ,2

Th e lowest mea n individu a l plasma co rti sol level s were reco rd ed during ex pos ure to th e hot- humid en vi ron men t a nd th e hig hes t in th e coo l-humid co nditi o ns. In c re ased THT va lu es were statis ti call y co rrela ted (? < 0·005) with d ec reased p las ma co rti so l levels. Th e three sh ee p which h ad hi g h p lasma co rti so l va lues co ns um ed less wa te r (?< 0·05) a nd h a d a low er urin e o utput (P < O·Ol) but a hig h e r PCV (P < O·OOI) th a n the three sh ee p whi ch h ad lower p lasma cort isol va lu es (Fig. I) wh en ex posed to eac h of th e fo ur env iro nm e nts. \l\lithin each env iron m ent, individu a l body weights were no t sign ifi ca ntl y d iffe ren t. Lin ea r regress ion a n a lyses s howed th a t in a ll the s hee p increased pla s ma co rti so l conce ntra tion was related to d ecreased wa ter int a ke in the hot- humid (P < 0·05) a nd hot-d ry (? < 0·00 5) environme nts, a nd to d ecreased urine ou tput in the ho t-humid (P < 0·05), hot-dry (P
Th e p las m a cort iso l co ncentra tion was d e te rmin ed in cat tle by Cabe ll o ( 1980) wh o reported values ranging between 22 ·4·5 a nd 160·05 nm o l/ 1. In ex p e rim e nt s with ca t tle, Hud so n et al. ( 1976) found a m ea n plasma co rti so l conce ntra ti o n of 6 ng/ ml. Dur ing stress st udi es with shee p , Ti lton el al. ( 1975) found pla sm a co rti so l va lu es th a t ra nged between 2·53 ng/ ml a nd 6·29 ng/ ml. The ra nge of plasm a corti so l co nce ntra ti o ns fou nd in the prese nt experim e nt were s imil a r to th ose fou nd in prev io us tr ia ls with rumin a n ts. During ex pos ure to a hot-humid e nvironm e nt , m ea n p las m a cortisol co nce ntrat io n decreased betw ee n 70 % a nd 96% when co mp a red with th e sa me va lue s found in coo ldry cond iti o ns. In creased THI va lues were co rrela ted (P < 0·005) with d ecreased pl as m a corti so l. Thes e fin d in gs merely co nfirm the resu lts of previou s tri a ls. In g ra h a m el al. ( 1979) fou nd th a t prolonged hea t expos ure d e pressed pl as m a co rti so l in cat t le; T il to n et al. ( 1975) found simi lar results in sheep. Of interest, however, was th e findin g th at p lasma cort iso l levels we re d epressed throu g hout ho t-humid expos ure. Thi s resu lt s uggested th a t ifTHT va lu es rem a in ed a bove 84, p las m a co rti so l re m a in ed depressed . P las m a co rti so l m ay have in c reased during th e firs t d ays of h ea t exposure as h as bee n previously obse rved in ca ttl e (A lva rez & J o hn so n , 19 73) a nd sh ee p (T il ton el a!., 197 5). In the pres ent ex pe rim ent pl as m a samples were no t co ll ected until seve n days a ft e r expos ure began, therefore , we were unab le to desc ribe a h ypot h et ica l in c rease of pl as m a cort iso l during the firs t days of heat ex posure. The ad rena l co rti so l di sch a rge durin g th e initi a l ph ases of h eat exposure may have acco unt ed fo r a n ult e rior d e pl e tion of th e horm o n e (Rh ynes & Ewin g, 1973). Thi s ph eno m e no n m ay exp la in w h y pl as m a cortiso l a pp ea red to d ec rease durin g prol o nged hea t ex posu re . Th e res u lts show th a t pl as m a co rti so l co nce ntra tio n de creas ed s ig nifica ntl y (P < 0·005) more durin g ex po sure to a ho t-h u mid environment t ha n to a ho t-dry one.

EN ViRO NMEN T AN D PLASMA CORTISOL I N SH EE P

18 1

This findin g s uggests th a t during h eat expos ure th e ve ry humid environm en t depressed co rti so l va lu es furth er . In a ddition , it und erlin ed the need to relate the TH I , a nd not a mbient tempera ture a lone, with blood para m e ters in o rd er to determine th e effects of clim a te on rumin a nts . In gram & M o unt (1975) fo und that sheep were less stressed in a hot-dry enviro nm ent than in a hot- humid one . I f th e ex tent o f the d ecrease in pl as ma co rti sol durin g h eat ex pos ure is a n acc ura te indi cation of the degree of chro nic stress in sh ee p , the res ults of th e present ex perim ent s uggest th at th e shee p were less stressed during th e ho t-dry env iro nm ent than during th e ho t-humid o ne . Th e lowest THI va lu es (63 to 65) w ere hig hl y co rrela ted (? < 0·005) with the hig hes t plas ma cortisol va lu es (66 to 96 nmol / 1). Simil a rl y, th e hig hest THI va lu es (84 to 88) were hig hly co rrel a ted with the lowes t pl as m a cort iso l va lu es (4 to 7 nmol / 1). In contras t, inte rmed iate THI va lu es (65 to 70) were not statisti ca lly re lated (P < 0·3) with interm ediate p las ma co rti so l va lu es (40 to 50 nmol/1). Th ese findin gs indi ca te th a t extrem e, rather th a n intermedi a te, THI va lu es were like ly to produ ce sig nifi ca n t cha nges in the pl as m a co rti sol va lu es of sh ee p . In o rd er th erefor e to induce sig nifi ca nt co rti co id cha nges due to ex posu re to diffe rent a mbi ent tempera tures a nd humidity , THI va lues a bove 80 o r below 60 sho uld b e so ug ht. Th e res ults a lso s how th a t the shee p which ha d hig h pl as m a co rti sol values co ns um ed less wa te r a nd had a lower urin e o u tput than sheep with hig h pl asma co rti so l levels. In additi o n , lin ea r regress ion a na lys is indi cates th at in creased pl as m a co r tiso l was co rrela ted with d ecreased wa ter inta ke (? < 0·005) a nd d ecreased urin e output (?< 0·005) in a ll th e shee p throughout th e ex perim ent. Th ese findin gs concur with those of Fa n et al. ( 1975) in ex pe rim ents o n shee p a nd those o f O 'Con no r & V ern ey ( 1942) who m a inta in ed th a t co rti coi d s exerted sig nifi ca n t sodium-re tai ning act ivity. Fan et al. ( 19 75) obse rved that wa ter in ta ke a nd urin a ry sod ium d ec reased in shee p whi ch had been infu sed w ith co rti co id s whil e at the sa m e time p las m a sod ium co nce ntra tion in c reased . In the prese nt ex perim ent , wa ter in take m ay have d ecreased when co rti so l in creased because water a nd sodium losses d ecreased . Th ese findings s ugges t th at hig h co rti so l leve ls exe rt sig nifi ca nt water a nd sodium -reta ining ac tivity during ex pos ure to coo l enviro nm ents. In co ntrast, in th e hot-humid environ m e nt , low co rti so l values m ay have bee n related to th e in creased urin e output a nd in creased urin a ry sodium losses o bse rved. It sho uld be noted th a t various a utho rs (C ollin s & W ein er , 1968; Thompson, 1973) reco rd th at sodium losses in creased in sh ee p exposed to hot en v iro nm ents. Th ese findin gs co ntras ts with the we ll- known ph e nom eno n of redu ct ion in sod ium loss in m a n when exposed to hot e nvironm ents. Th e prese nt expe rim ent shows th a t in c reased pl as m a co rti so l is co rrelated w ith a n in creased PCV (P< O·OO I ). Th e lin ea r relat io nship be tw ee n th ese pa ra m ete rs was sign ifi ca nt d urin g each ex pos ure peri od. Thi s findin g indi cates th at pl as m a cortiso l cha nges caused by environ m enta l m odifi cat io ns we re ab le to a ffec t red bl ood ce ll produ ct io n o r PCV . Lee et al. ( 1976) observed simil a r effects in cat tl e. Th e res ults of the present ex p erim ent s uppo rt th e we ll- es ta blis hed co nce p t that cort iso l in creases red bl ood ce ll produ cti o n (G u y to n , 197 1). The hi g hly sig nifi ca nt co rre latio n found between pl as m a cortisol a nd PCV s ugges ts th at PCV m ay be a n acc ura te m eas ure o f p las m a co rti so l a nd hen ce of the st ress stat us o f rumin a n ts. Th e determinat io n of plas ma co rti so l leve ls therefore sho uld be accompan ied by a n assess m ent o f PCV during hea t-s tress s tudi es in rumin a nts.

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{r1ccej;/ed for jmblicalion 14 Jul.J' /981)

ANNOUNCEMENT TH I RD WORKSHOP ON H ORMONES IN fv!ILK

following the two successful Vl o rks ho ps held in London ( 1976) and Nottingham ( 1979) a third meeting is plan ned for T hu rsday, 15 Apri l 1982 to be held in the Conference Centre, A.R.C. In st itute of Animal Physiology , Babraham, Cambridge. The programme wi ll in clud e papers on methodology, and a pp li catio ns o f mi lk progeste rone and milk oest roge n tests. For further deta il s please contact: Dr R. B. H eap, A.R.C. Institute of Animal Phys iology, Babraham , Cambridge CB2 4A T.