EFFECTIVENESS AND USES OF BIODEGRADABLE HYDRAULIC LIQUIDS
J. Pošta, R. Zewdie
Czech University of Agriculture, Faculty of Engineering, Prague, Czech Republic
Biodegradable hydraulic liquid of vegetable origin decreases the contamination of life environment. This paper shows the scope of the diagnostic following the alterations of influencing these liquids during the operation and the design methodology of optimal administration for their recovery.
biodegradable hydraulic liquid; content of contaminants; viscosity; regime of wear out; diagnostic signal
INTRODUCTION
The replacement of crude oil products by other materials is currently motivated above all by the search to acquire materials with better ecological character and utilize a part of The Agricultural Fund for non-agricultural objects. One of the obstacles to wide usage and application of biodegradable hydraulic liquids are currently the undefined and unclarified questions concerning its utility and effectiveness.
The use of hydraulic equipment in tractors, mobile technology, agricultural and construction machines, etc. presents a serious threat to the environment because of oil losses in the fields which lead to the contamination of water and soil (Pošta, 1995; Chrást et al., 1995). In the same way thousands of tons of fossil oil products enter the soil and water annually. This leads, together with construction solutions, to look for an alternative method of reduction of harmful effect, acceptable biodegradable hydraulic liquid that does not, in case of leakage, cause large damage and protects the environment.
Along with the use of a biodegradable hydraulic liquid in the hydraulic system of a machine together with the presently used classical mineral oil as a complex it is possible to predict (Zewdie, 1997; Hartweg et al., 1989):
The objective of this contribution is to adapt the theoretical and methodical analysis of a given problem concerning total techno-economical effectivity.
MATERIAL AND METHOD
To reach the established objective of the work it is necessary to:
The renewal (replacement) of liquids in a hydraulic system could be understood as an optimization normative for a renewal, extension or a reduction of the interval in which the exploited liquid has an impact on the total effectiveness. The contribution analyzes this problem from techno-economical point of view which includes all influences connected with the discharged liquids, due to different wear out intensity of elements of hydraulic aggregates and with respect to ecological requirements.
THEORETICAL PRINCIPLES OF SOLUTION
Professional literature substantiated that the effectivity of technical object is determined by the sum of acquisition (production) and operational costs to its lifetime per unit (number of km, work done, production etc.). It means, we are talking about the so called average unit price of a given technical object (Pošta, 1993; Havlíèek et al., 1989).
If the condition of technical object is evaluated by the change of a selected diagnostically signal S, as the indicator of the effectivity of the object the renewal time is determined by a hidden value So of a given signal, then the ratio of the sum of acquisition and operational cost to its lifetime is minimal.
The operational costs are supposed to increase with the increasing volume of the work performed (i.e. with increasing time of operation), due to failure mechanisms. If the result in form of the average unit costs of renewal and operation of the equipment can be identified with sufficient accuracy with the similar value of the selection set, then the selected diagnostic signal can be stated, (Havlíèek et al., 1989)
(1)
where:
u(S) = mean value of the average unit costs of the renewal and the operation of the equipment when reaching the technical state S
n = range of the selection set (number of investigated elements)
Noi = costs of the renewal of the i-th element
Npi(S) = costs of the operation of the i-th element from the beginning to reaching the S state or till the necessary putting out of the operation before reaching the S state
ti(S) = operational time of the i-th element from the beginning up to the S state or physical life of the i-th element, which did not survive up to the S state
As every discrete value Si of the diagnostic signal has the corresponding variable operational times for the respective element ti(Si), from which it is possible to calculate the mean value t(Si), to determine the function t(S), Fig. 1, and after a statistical evaluation, the equation (1) can be transformed to a general form of the effective function of renewal
(2)
where:
u(t) = mean value of the average unit costs of the renewal and the operation of the equipment when reaching the S technical state, or t(S) = t
No = mean costs of the renewal of the equipment
t(S) = t = mean operational time of elements up to the S state
Np(t) = mean cumulative operational cost up to the S state, or t(S) = t
vp(t) = mean instantaneous costs of the operation till the S state, or t(S)
As the unit renewal costs uo(t) = No t -1 are a permanently decreasing function of the mean operational time and the unit operational costs are an increasing function, the summary function u(t) has a local minimum u(tO), whose coordinates are dependent on the items, that form the function (1) or (2), and obtaining them is the general purpose of the whole optimization solution.
The methods of the determination of the standard for the liquid renewal in a hydraulic system should therefore be as follows:

Fig. 1 The principle of the assignation of the optimal value of the diagnostic signal of preventive replacement
EXPERIMENTAL VERIFICATION
To obtain the necessary source materials for the verification of the possibility of the application of the above mentioned theoretical constructions, the laboratory test of the hydraulic system was carried out with biodegradable liquid of Czech production. Observed were the changes of selected parameters characteristic for the technical state of the hydraulic system as well as for the liquid:
The analyses were carried out repeatedly, the gained results were statistically evaluated.
The testing equipment consisted of two basic units, that were formed by a high-pressure hydraulic aggregate and a loading equipment. The scheme is given in Fig. 2.

Fig. 2 Scheme of laboratory apparatus
1, 15 = basin 2 = filter 3 = hydraulic pump 4 = electric motor
5 = clack-valve 6 = insurable (pressure) outlet 7, 8, 14 = conveyance 9 = alteration switch 10, 11 = hydraulic motor 12 = barometer 13 = adjustable outlet 16 relay
The testing equipment was adjusted for automatic operation. Operational times, the pressures at measurement points, the number of cycles, and the temperature of hydraulic liquid were continuously monitored.
The first stage of the experiment was carried out for 400 hours (120 000 loading cycles). The control samples of the liquids were extracted every 50 hours of operation. During the experiment the temperature in the primary circuit was maintained on 54 ± 3 oC. The loading pressure was set on 14 Mpa.
RESULTS
A number of particular data were obtained during the experiment. An example can be given by the data relating to the parameter “total content of contaminants”, see Table 1.
Table I Experimental ascertained and rated values
|
t |
h |
0 |
50 |
100 |
150 |
200 |
250 |
300 |
350 |
400 |
|
S = CN |
% |
0,015 |
0,046 |
0,106 |
0,140 |
0,154 |
0,197 |
0,240 |
0,266 |
0,292 |
|
No/t(S) |
Kc/h |
90,04 |
45,02 |
30,01 |
22,51 |
18,01 |
15,01 |
12,86 |
11,25 |
|
|
Np[t(S)]/t(S) |
Kc/h |
0 |
0,007 |
0,051 |
0,075 |
0,115 |
0,135 |
0,183 |
0,251 |
0,268 |
|
u[t(S)] |
Kc/h |
90,047 |
45,071 |
30,085 |
22,625 |
18,145 |
15,193 |
13,111 |
11,518 |
It is apparent during this experiment that the minimum sum function was not accomplished. Behalf the chance attestation applicability of a designed methodology have been accordingly experimental data replaced by a theoretic function. The sum function has been expressed in common conformation
(3)
where:
u(S) = mean value of the average unit costs of the renewal and the operation of the equipment when reaching the technical state S
No = mean costs of the renewal of the equipment
S = diagnostic signal
a1, b1, a2, b2 = parameters of a theoretic sum function
For the assignation of arguments and indexes of the correlation of the theoretic sum function was applied the standard method of correlation and regression analyses. It is apparent, that designed theoretic functions are very well described by experimental data. By the extrapolation of a theoretic function these were assigned optimal values for recovery of hydraulic oil. It is once again an exigency to admonish, that those values need additional experimental acknowledgment.
Table II Parameters and correlation indexes of theoretic functions
|
a1 = 5205,8321 |
a2 = 1575,9358 |
|
b1 = 3,0931 |
b2 = 1,1512 |
|
r1 = 0,9966 |
r2 = 0,9915 |
Under equation (3) there were rated theoretic values of a sum function behalf diagnostic signal S1 = content of aggregate contamination and S2 = operating time. Values of u(S)T of theoretic and values u(S)E of experimental function are in a table III and pictures 3 and 4. Appropriate values of diagnostics signals (@ S1) and (@ S2) are assigned by a linear interpolation.
Table III The values of the function u(S1), u(S2)
|
u(S1) |
u(S2) |
||||||
|
S1 |
u(S1)E |
u(S1)T |
@ S2 |
S2 |
u(S2)E |
u(S2)T |
@ S1 |
|
% |
Kc/h |
Kc/h |
h |
h |
Kc/h |
Kc/h |
% |
|
0,05 |
89,86 |
89,99 |
50,1 |
50 |
90,05 |
91,70 |
0,05 |
|
0,1 |
40,21 |
40,50 |
111,3 |
100 |
45,07 |
45,05 |
0,09 |
|
0,15 |
25,43 |
25,45 |
177,4 |
150 |
30,09 |
30,08 |
0,13 |
|
0,2 |
18,32 |
18,36 |
247,1 |
200 |
22,63 |
22,61 |
0,17 |
|
0,25 |
14,27 |
14,32 |
319,5 |
250 |
18,15 |
18,16 |
0,20 |
|
0,3 |
11,64 |
11,74 |
394,1 |
300 |
15,19 |
15,21 |
0,24 |
|
0,35 |
- |
10,00 |
470,6 |
350 |
13,11 |
13,12 |
0,27 |
|
0,4 |
- |
8,76 |
548,8 |
400 |
11,52 |
11,58 |
0,30 |
|
0,45 |
- |
7,86 |
628,5 |
450 |
- |
10,40 |
0,34 |
|
0,5 |
- |
7,21 |
709,6 |
500 |
- |
9,48 |
0,37 |
|
0,55 |
- |
6,72 |
791,9 |
550 |
- |
8,75 |
0,40 |
|
0,6 |
- |
6,37 |
875,3 |
600 |
- |
8,15 |
0,43 |
|
0,65 |
- |
6,12 |
959,8 |
700 |
- |
7,27 |
0,49 |
|
0,7 |
- |
5,96 |
1045,2 |
800 |
- |
6,68 |
0,55 |
|
0,75 |
- |
5,87 |
1131,6 |
900 |
- |
6,29 |
0,61 |
|
0,8 |
- |
5,84 |
1218,9 |
1000 |
- |
6,04 |
0,67 |
|
0,85 |
- |
5,85 |
1307,0 |
1100 |
- |
5,89 |
0,73 |
|
0,9 |
- |
5,92 |
1395,3 |
1200 |
- |
5,84 |
0,79 |
|
0,95 |
- |
6,02 |
1485,6 |
1300 |
- |
5,85 |
0,85 |
|
1,0 |
- |
6,16 |
1575,9 |
1400 |
- |
5,92 |
0,90 |
SUMMARY
Besides the characteristics of the biodegradable liquids at the moment of their production, there is very important there are also changes of these characteristics during the operation. The knowledge of these relations is necessary for the control of the optimal replacement of liquids.
The performed experiments have proved the possibility of the monitoring and the usage of the selected parameters of the technical states of the hydraulic system with a biologically degradable liquid. The selected parameters and the method of their determination are therefore suitable for this purpose.
We can recommend the following procedure to the users who want to achieve an optimal control of renewal of biodegradable hydraulic liquids:
REFERENCES
EFFECTIVENESS AND USE OF BIODEGRADABLE HYDRAULIC LIQUIDS
Address of authors
Doc. ing. Josef Pošta, CSc.
Dr. ing. Retta Zewdie
technická fakulta
Èeská zemìdìlská univerzita v Praze
Kamýcká 129
165 21 Praha 6 - Suchdol
Tel. 02/24383266
E-mail: POSTA@TF.CZU.CZ
EFFECTIVENESS AND UTILITY OF BIODEGRADABLE HYDRAULIC LIQUIDS
EFEKTIVITA UŽITÍ BIOLOGICKY ODBOURATELNÝCH HYDRAULICKÝCH KAPALIN
SOUHRN
Náhrada ropných produktů jinými vhodnými materiály je motivována především snahou získat materiály s lepšími ekologickými vlastnostmi, snížit závislost na producentech ropy a využít zemědělskou půdu pro nepotravinářské účely.
Použití hydraulických zařízení u mobilní techniky, především u traktorů, užitkových vozidel, zemědělských a stavebních strojů atd. v sobě skrývá mimořádné riziko znečištění vody a půdy při ztrátách hydraulických kapalin v terénu.
Při použití biologicky odbouratelných kapalin v hydraulických soustavách strojů lze při komplexním pohledu, při porovnání s dosud užívanými minerálními kapalinami, očekávat (
Zewdie, 1997; Hartweg et al., 1989):Teoretické a metodické zpracování problému celkové technicko ekonomické efektivity užití biologicky odbouratelných hydraulických kapalin bylo cílem práce. Pro jeho dosažení bylo nutno:
V odborných publikacích je dostatečně zdůvodněno, že vhodným integrálním ukazatelem efektivnosti užití technického objektu je suma pořizovacích (výrobních) a provozních nákladů, připadajících po vyčerpání technického života objektu na jednotku jeho doby provozu. Jedná se ukazatel “průměrné jednotkové náklady”, (
Pošta, 1993, Havlíček et al., 1989;). Toto kriterium bylo použito i v této práci.Pro stanovení normativu pro výměnu (obnovu) biologicky odbouratelné kapaliny v hydraulické soustavě byl navržen tento postup:
Bylo navrženo a vyrobeno laboratorní zkušební zařízení, které umožnilo sledování a registraci všech potřebných údajů. Zařízení je schematicky znázorněno na obrázku 2.
Při tomto experimentálním ověřování byly sledovány tyto diagnostické signály:
Byla získána experimentální data, která byla zpracována podle navržené metodiky. Výsledky, vztahující se k nejvhodnějšímu diagnostickému signálu jsou uvedeny v tabulkách I až III a graficky znázorněny v obrázku 3.
Jako nejvhodnější a nejpřesnější diagnostický signál se v podmínkách experimentu ukázal “celkový obsah nečistot”. Pro tento signál byly zpracovány všechny zjištěné údaje, stanovena teoretická závislost na době provozu a určen normativ pro výměnu kapaliny. Byla potvrzena vhodnost a reálnost použití navržené metodiky pro optimální výměnu hydraulické kapaliny a pro hodnocení celkové efektivity užití biologicky odbouratelných hydraulických kapalin.
Uživatelům hydraulických zařízení s biologicky odbouratelnou hydraulickou kapalinou lze doporučit následující postup optimálního řízení výměny kapaliny:
biodegradovatelná hydraulická kapalina; viskozita; obsah nečistot; režim opotřebení; diagnostický signál
SUMMARY
The compensation of oil products in different suitable materials is motivated first of all by the effort to discover materials with better ecological properties, to lessen the dependence on producers of oil and cultivate agricultural land for non food purposes.
The use of the hydraulic appliances in mobile machinery, especially with tractors, utility vehicles, agricultural and construction machines, etc. conceals an extraordinary risk in the pollution of water and soil from leakage of hydraulic liquids in the field.
During the use of biodegradable liquids in the hydraulic systems of machines it is possible at complex view when making comparison with current mineral liquids, expect (Zewdie, 1997; Hartweg et al., 1989):
Theoretical and methodical process of the problem of overall technical-economical effectiveness in the use of biodegradable hydraulic liquids was the primary object of the work. To reach a conclusion it was necessary:
In professional publications it is sufficiently stressed that a suitable integral indicator of the effectiveness of the use of technical object is the sum of entry (production) and operational costs resulting after the exhaustion of the technical duration time of the object in the unit at the time of operation. It is the question of the indicator “average unit expenses” (Pošta, 1993; Havlíèek et al., 1989). This criterion was also used in this work.
For the determination of the normative for the exchange (restoration) biodegradable liquid in the hydraulic system the following method was proposed:
It was proposed and produced a laboratory experimental appliance which made it possible to observe and register all required data. The appliance is schematically demonstrated in picture 2.
During this experiment verification was followed by these diagnostic signals:
There were obtained experimental data which were processed according to suggested methodics. The results in relation to the most suitable diagnostic signal are presented in tables I up III and graphically demonstrated in picture 3.
As the most suitable and the most accurate diagnostic signal appeared in the conditions of the experiment “overall content of impurities”. For this signal there were processed all figured out data, stated theoretical dependence on the time of the operation and determined normative for the change of the liquid. There was confirmed the suitability and reality for the use of the proposed methodics for optimal change of hydraulic liquid and for the evaluation of overall effectiveness and the use of biodegradable hydraulic liquids.
To those using hydraulic appliances with biodegradable hydraulic liquid is now possible to recommend the following procedure of the optimal regulation in the change of the liquid:
biodegradable hydraulic liquid; viscosity; content of impurities; regime of wear out; diagnostic signal